Refine
Year of publication
Document Type
- Doctoral Thesis (47)
Has Fulltext
- yes (47)
Is part of the Bibliography
- no (47)
Keywords
Heutzutage unterliegen insbesondere aquatische Ökosysteme durch den permanenten Anstieg nicht-heimischer Arten einem folgenreichen Wandel. Dabei stellt der Biodiversitätsverlust nur den Endpunkt einer biologischen Invasion dar. Dazwischen wirken sich Faktoren wie Konkurrenz-, Prädationsdruck oder die Übertragung von Krankheitserregern wie z.B. Parasiten auf den Rückgang der Arten aus. Als integraler Bestandteil eines jeden Ökosystems spielen Parasiten bei Invasionsprozessen eine entscheidende Rolle und können durch ihren Einfluss auf heimische und nicht-heimischen Arten Invasionen begünstigen. Fische übernehmen aufgrund ihrer vielseitigen Bedeutung im Nahrungsnetz eine Schlüsselfunktion als Wirte diverser Parasitenarten und sind deshalb ausgezeichnete Untersuchungsobjekte, um durch nicht-heimische Arten verursachte Veränderungen in Nahrungsnetzstrukturen oder Parasitenfaunen aquatischer Ökosysteme aufzudecken.
Vor diesem Hintergrund wurde die vorliegende kumulative Dissertation angefertigt, welche auf drei (ISI-) Einzelpublikationen basiert. Die Arbeit beschäftigte sich unter Verwendung morphologischer und molekularbiologischer Methoden schwerpunktmäßig mit der Parasitendiversität und Nahrungsökologie zweier eingeschleppter Fischarten in stark anthropogen beeinflussten deutschen Fließgewässern. Dabei handelte es sich um die hauptsächlich durch das Ballastwasser von Schiffen verbreitete invasive Schwarzmundgrundel Neogobius melanostomus aus den Flüssen Rhein und Main sowie den von Hobby-Aquarianern in den durch Industrieabwässer thermisch belasteten Gillbach ausgesetzten Zebrabuntbarsch Amatitlania nigrofasciata. Unter Berücksichtigung nahrungsökologischer und räumlich-zeitlicher Aspekte sollten die parasitologischen Risiken und Konsequenzen, welche durch das Einschleppen nicht-heimischer Fischarten auftreten, aufgezeigt werden, um übergeordnet die Folgenabschätzung auf dem Gebiet der Invasionsbiologie zu verbessern. Das Nahrungsspektrum beider Fischarten wies sowohl räumliche (zwischen den Flüssen und Standorten), als auch zeitliche (monatlich) Variationen auf, was die Anpassungsfähigkeit bzw. die optimale Nutzung zur Verfügung stehender Ressourcen von invasiven Arten verdeutlicht. Ebenso wurden Unterschiede in der Parasitierung nachgewiesen, was die Notwendigkeit räumlicher und zeitlicher Analysen zur Erfassung der vollständigen Parasitenfauna einer invasiven Art, inklusive aller Variationen der Befallszahlen, unterstreicht. Beide Fischarten bilden zudem Zwischenwirte für heimische, als auch nicht-heimische Parasitenarten, wobei die direkte Einschleppung von nicht-heimischen Parasiten aus dem ursprünglichen Verbreitungsgebiet der Fische auszuschießen ist und somit die Enemy-Release-Hypothese (Verlust ursprünglicher Gegenspieler wie Prädatoren oder Parasiten) unterstützt. Dies könnte zusammen mit der opportunistischen Ernährungsweise ein Grund für die starke Ausbreitung sowie die anhaltend hohen Individuenzahlen dieser Arten im jeweils betrachteten Verbreitungsgebiet (Rhein, Main sowie Gillbach) sein.
Besonders hervorzuheben ist der Nachweis der nicht-heimischen Nematoden Anguillicoloides crassus und Camallanus cotti. Durch die Aufdeckung einer besonderen Form von Hyperparasitismus konnten erstmalig hohe Befallszahlen von A. crassus in N. melanostomus dokumentiert werden. Die hoch abundante Grundelart gilt somit potentiell als entscheidender Überträger des invasiven Parasiten auf den Europäischen Aal. Der durch seine hohe Virulenz in der Aquaristik bekannte C. cotti gelangte durch das Aussetzen von Zierfischen in den Gillbach und trat mit hohen Befallszahlen in A. nigrofasciata auf und wird bereits auf die heimische Fischfauna übertragen (z.B. auf den Gründling Gobio gobio und den Döbel Squalius cephalus). Ebenso ist der starke Befall der heimischen Parasiten Pomphorhynchus sp. (Acanthocephala) und Raphidascaris acus (Nematoda) bei N. melanostomus sowie A. anguillae (Acanthocephala) bei A. nigrofasciata zu nennen. Durch die zusätzliche Wirtfunktion der Neozoen und die hohen Befallsintensitäten ist mit einem verstärkten Spillback-Effekt (Rückinfizierung) auf heimische Fischarten zu rechnen.
Die stetig steigende Anzahl biologischer Invasionen führt zu immer weitreichenderen Veränderungen heimischer Ökosysteme. Für den Erhalt der Biodiversität sowie einhergehender Ökosystemfunktionen rückt auch die Forschung über Neobiota immer mehr in den Mittelpunkt. In diesem Zusammenhang gewinnen auch Pathogene wie Parasiten immer mehr an Bedeutung, welche durch gebietsfremde Arten eingeschleppt werden und die bestehende Biodiversität gefährden können. Die Ergebnisse der durchgeführten Studien haben gezeigt, dass die Verknüpfung von parasitologischen und nahrungsökologischen Untersuchungen Einblicke in die hoch dynamischen Prozesse der Invasionsbiologie geben können, was ein Vorantreiben der Forschung und Folgenabschätzungen auf diesem Gebiet ermöglicht.
Terrestrische Säugetiere werden von unterschiedlichen Parasiten als Wirte genutzt. Dabei kann ihre Parasitenfauna je nach Art, Lebensweise, Verbreitung, Gesundheitszustand und Reproduktionsstatus des Wirts abweichen. Ein weiterer bestimmender Faktor, ist der Einfluss des Menschen in Form von Regulierungsmaßnahmen und Schaffung urbaner Lebensräume. Domestizierte Haustiere bzw. Nutztiere weisen daher in der Regel andere Parasiten auf als ihre wildlebenden Artgenossen. Gleichzeitig können sich sowohl Wildtiere als auch domestizierte Tiere und Menschen gegenseitig Parasitenarten teilen und wechselseitig aufeinander übertragen. Daraus resultierende Krankheiten werden als Zoonosen bezeichnet.
Insbesondere Fledermäuse (Unterordnung Microchiroptera) zeigen weltweit eine enorme Parasitendiversität, die noch weitgehend unerforscht ist. Ebenfalls Forschungsbedarf besteht für die Sandfloh-Gattung Tunga in Süd- und Mittelamerika in Hinblick auf ihr Wirtsspektrum, welches auch Menschen einschließt. Die Art Tunga penetrans und zahlreiche weitere Parasitenarten, parasitieren gleichzeitig auch bei Hunden. Daher stellen diese Wirte eine direkte Gesundheitsgefahr für Menschen in ihrer unmittelbaren Umgebung dar.
Die vorliegende Dissertation ist in kumulativer Form zusammengefasst und beinhaltet drei Einzelpublikationen sowie einen Reviewartikel.
Ziel war es, die Parasitendiversität von Hunden aus urbanen tropischen Gebieten und die Parasitendiversität des Großen Ameisenbären (Myrmecophaga tridactyla) mit Hilfe morphologischer und molekularbiologischer Methoden zu analysieren. Die jeweiligen Parasitenfaunen wurden in Hinblick auf die soziale bzw. solitäre Lebensweise der beiden Wirtsarten verglichen und ihr zoonotisches Potenzial bewertet.
Ein weiteres Ziel war die Zusammenfassung der Ektoparasitennachweise süd- und mittelamerikanischer Microchiroptera und für die europäischen Arten der Fledermaus-Gattung Myotis (hier Endo- und Ektoparasiten) auf Basis der verfügbaren Literatur. Des Weiteren sollten eigene Parasitennachweise aus Bolivien bzw. Deutschland erfolgen. Für die Nachweise aus Deutschland wurden M. myotis untersucht, deren Artzugehörigkeit vorher bestimmt wurde. Zusätzlich wurden diese Individuen auf humanpathogene Lyssaviren untersucht.
Die Nachweise erfolgten über molekularbiologische und morphologische Methoden.
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.
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.
Occurrence and sources of 2,4,7,9-tetramethyl-5-decyne-4,7-diol (TMDD) in the aquatic environment
(2011)
The aim of the present study was to identify the sources of 2,4,7,9-tetramethyl-5-decyne-4,7-
diol (TMDD) into the aquatic environment and to investigate its occurrence in rivers and
wastewater treatment plants (WWTPs). Therefore, TMDD was analyzed in 441 wastewater
samples from influents and effluents of 27 municipal WWTPs, in 6 sludge samples, in 52
wastewater samples from 3 sewage systems of municipal WWTPs, in 489 surface samples
from 24 rivers, in 9 wastewater samples of 3 paper-recycling industries and in 65 groundwater
samples. TMDD was also analyzed in household paper products, in 23 samples of toilet
papers, in 5 types of paper towels and in 12 types of paper tissues. The samples were collected
between 2007 and 2011. The water samples were extracted with solid phase extraction (SPE)
and the household paper samples with Soxhlet extraction. Gas chromatography-mass
spectrometry (GC-MS) was used for quantification purposes.
Between November 2007 and January 2008, TMDD was detected in the river Rhine at Worms
with permanent high concentrations (up to 1330 ng/L). The results showed that TMDD is
uniformly distributed across the river at Worms. An increase of the mean TMDD
concentration from approximately 500 ng/L to 1000 ng/L was registered in January 2008. Due
to the minor fluctuations of the TMDD concentration during the sampling period it is
expected that the input of TMDD into the river is continuous. Therefore, TMDD might rather
originate from effluents of municipal WWTPs than from temporal sources. The mean TMDD
load based on the analysis of 147 water samples collected in the River Rhine was 62.8 kg/d
which is equivalent to 23 t/a suggesting that TMDD must be used and/or produced in high
quantities in order to be found in those high concentrations. To determine if TMDD is
discharged by effluents of municipal WWTPs into the rivers, 24 hours influent and effluent
samples of four municipal WWTPs in the Frankfurt/Rhine-Main metropolitan region were
collected during November 2008 and February 2010 and analyzed for TMDD. The TMDD
influent concentrations varied between 134 ng/L and 5846 ng/L and the effluent
concentrations between <LOQ (limit of quantitation) and 3539 ng/L. The TMDD elimination
rates in the four WWTPs varied between 33% and 68%. The results showed that effluents of
municipal WWTPs are an important source of TMDD in the aquatic environment because
TMDD is not completely removed from the sewage during the wastewater treatment. Weekly
and daily variations of the TMDD concentration in the influents of two municipal WWTPs
indicated that both private households and indirect industrial dischargers contribute to the
introduction of TMDD into the municipal sewage systems. A more detailed study of the
TMDD elimination rate in the different wastewater treatment stages was carried out in the
WWTP Niederrad/Griesheim in Frankfurt am Main. The results showed that the removal of
TMDD is mainly carried out during the aerobic biological treatments, where the elimination
rate was 46%. In contrast, during the anoxic treatment the removal efficiency was only 1.4%
and during the mechanical treatment the elimination rate was 19%.
To determine the sources of TMDD in the sewage, household paper products (paper tissues,
toilet papers and paper towels) were analyzed for TMDD using Soxhlet extraction. TMDD
was detected in 83% of the samples (n=40). The highest mean TMDD concentrations were
found in recycled toilet paper (0.20 μg/g) and in paper towels (0.11 μg/g). In paper tissues and
non-recycled toilet paper the mean TMDD concentrations were lower 0.080 μg/g and
0.025 μg/g respectively. According to these results the high TMDD influent concentrations
found previously in municipal WWTPs (mean 1.20 μg/L) cannot be explained due to
migration of TMDD from the household paper products into the sewage. Thus indirect
industrial dischargers are the cause of the high influent TMDD concentrations. Effluents of
municipal WWTPs with different indirect industrial dischargers (textile-, metal processing-,
food processing-, electroplating-, paper-recycling- and printing ink factories) were analyzed.
The highest mean TMDD concentrations were found in the effluents of municipal WWTPs
that have paper-recycling (71.3 μg/L) and printing ink factories (138 μg/L) as indirect
industrial dischargers. These results were confirmed by analyzing process wastewater of three
paper-recycling factories located in Germany. High TMDD concentrations were detected and
fluctuated between 1.83 μg/L and 113 μg/L. TMDD was also analyzed in the wastewater of a
non-recycling-paper factory but its concentration was much lower (0.066 μg/L) indicating that
TMDD is introduced into the processing water during the papermaking process due to the use
of waste paper. Analyses of wastewater samples from different parts of the sewage pipes of a
municipal WWTP in Hesse, which receives the wastewater from a printing ink factory, were
carried out. The TMDD concentration in the wastewater sample from the sewage pipe of the
printing ink factory was much higher (3,300 μg/L) than the TMDD concentration detected in
the other wastewater samples from the sewage system (0.030 μg/L – 0.89 g/L). These results
confirm the printing ink production as one of the principal sources of TMDD in the sewage.
Analysis of surface water samples of the River Modau downstream from the effluent of the
WWTP Nieder-Ramstadt showed TMDD concentrations of up to 28.0 μg/L. These high
TMDD concentrations might be caused by the indirect wastewater discharges of a paint
factory connected to the municipal sewage system. These results indicate that TMDD is
introduced into the municipal WWTPs principally by indirect industrial dischargers and they
are mainly paint and printing ink factories. The paper-recycling factories also represent an
important source of TMDD in municipal WWTPs but indirectly. According to statements
given by the representatives of two paper recycling factories neither TMDD or any other
TMDD containing product is used or added during the papermaking process. Therefore,
TMDD is washed out from the printing inks of the coloured waste paper and concentrated in
the process wastewater in the closed water circuits of paper-recycling factories reaching rivers
and municipal WWTPs.
The occurrence and distribution of TMDD in surface waters in Germany was also studied.
The results showed that TMDD is widely distributed across different rivers systems in the
federal states of Hesse, North-Rhine-Westphalia, Bavaria, Baden-Wuerttemberg and
Rhineland-Palatinate. In Hesse, TMDD was detected in the some of main rivers with mean
concentrations of 812 ng/L (Schwarzbach, Hessian Ried), 374 ng/L (Kinzig), 393 ng/L (Main,
at Frankfurt), 539 ng/L (Werra), 326 ng/L (Fulda), 151 ng/L (Emsbach) and 161 ng/L
(Nidda). In small rivers (creeks) the mean TMDD concentrations varied between <LOQ
(Diemel, Urselbach) and 1890 ng/L (Darmbach). The results showed that the TMDD
concentrations in creeks are highly influenced by both effluents of WWTPs and by the
distance between the sampling point and the nearest WWTP. Surface samples from sampling
locations downstream from WWTPs dischargers showed higher TMDD concentrations (mean
518 ng/L) than sampling locations upstream from WWTPs dischargers (mean 35.1 ng/L).
The behavior of TMDD during bank filtration was investigated at two locations, at a water
utility company at the Lower River Rhine (urban area) and at the Oderbruch polder (rural
area). The results indicated that TMDD is removed from the surface water by bank filtration
at both sampling locations. The removal process is probably carried out in the first meters of
the aquifer (hyporheic zone) by biodegradation processes, since TMDD does not tend to be
absorbed by sediments and it was not found in the groundwater of monitoring wells. In
groundwater samples from the Hessian Ried (n=23) TMDD was found only in five samples
and the highest TMDD concentration was 135 ng/L. According to these results, TMDD does
not represent a concern for drinking water in Germany, since it does not reach the
groundwater with high concentrations and it has a low toxicity potential.
The input of TMDD into the North Sea was estimated to be 60.7 t/a by considering the mean
transported loads of TMDD by the River Rhine at Wesel (58.3 t/a) and Meuse in the
Netherlands (2.40 t/a). The estimated discharge of TMDD by German municipal WWTPs
(8.19 t/a) and paper-recycling factories (9.24 t/a) into rivers seems to be too low considering
that the mean TMDD load in the River Rhine downstream from Wesel is 58.3 t/a. However,
due to the high density of population and industries at the Lower Rhine it is expected that
more relevant sources of TMDD are located along the Rhine River increasing the transported
load.
According to the results of this PhD project TMDD is a non-ionic surfactant contained in
products, which are applied on surfaces (printing inks and paints) and has the potential to
reach the aquatic environment. Therefore, TMDD should fulfill the requirement of a
biodegradability of 80% established by the “Law on the Environmental Impact of Detergents
and Cleaning Products” in Germany. However, due to the partial elimination rates of TMDD
obtained in municipal WWTPs (between 33% and 68%) and to the absence of information
about the execution of the biodegradation test on TMDD, it is unknown if TMDD is in
accordance with this law. Otherwise, its use as surfactant in such products is questionable.
Ziel der vorliegenden Arbeit war es, vor- und nachbereitenden Unterricht zu Biodiversitätsführungen an den vier außerschulischen Lernorten Palmengarten, Senckenbergmuseum, Stadtwaldhaus und Zoo Frankfurt zu evaluieren. Durch den Unterricht mithilfe neu entwickelter Arbeitsmaterialien sollte die aktuelle Motivation der Schüler und weitere pädagogisch-psychologische Lernvariablen gefördert werden. Es stellte sich die Frage, ob so eine erhöhte Auseinandersetzung mit dem Themenkomplex Biodiversität erreicht werden kann und welche Einflussfaktoren dabei eine Rolle spielen.
Theoretische Grundlage war dabei das Risikowahlmodell der Leistungsmotivation nach Atkinson, das von Rheinberg zum handlungstheoretischen Modell der Motivation erweitert wurde (Rheinberg & Vollmeyer, 2012). Auf dieses bezieht sich der von Rheinberg et al. (2001) entwickelte und hier eingesetzte Fragebogen zur aktuellen Motivation (FAM).
Die Stichprobe setzte sich aus insgesamt 523 Schülern der Klassen 5 bis 9 zusammen. Davon nahm jeweils die Hälfte mit (Versuchsgruppe) und die andere ohne (Kontrollgruppe) vor- und nachbereitendem Unterricht an den Biodiversitätsführungen teil. Die Erhebung der aktuellen Motivation, des erworbenen Fachwissens und weiterer Variablen erfolgte in einem Pre/Post/Follow-Up-Design mit Fragebögen, deren Auswertung analytisch statistisch durgeführt wurde.
Es zeigte sich, dass in der Gesamtstichprobe die Teilnahme an der Biodiversitätsführung die aktuelle Motivation der Schüler erhöhte. Dauerhafte Lernparameter wie die Biologieeinstellung und die Interessenshandlung wurden jedoch nicht signifikant verändert. Ein eindeutiger Effekt der unterrichtlichen Vorbereitung konnte jedoch nicht ermittelt werden. Einzig beim gemessen Fachwissen zu den Führungsinhalten schnitt die Versuchsgruppe signifikant besser ab. Insgesamt wird angenommen, dass der Effekt des Besuchs des außerschulischen Lernortes an sich den Effekt der Vor- und Nachbereitung überdeckt oder vom Einfluss anderer Parameter beeinflusst wird. Hier stach besonders das Alter der Jugendlichen hervor, das vor allem in der hier evaluierten Schülergruppe bedingt durch die Pubertät eine große Rolle spielt. Weitere Einflussfaktoren waren die Biologieeinstellung und die Unterrichtsvariablen der Führung. In den Stichproben der einzelnen außerschulischen Lernorte zeigten sich leichte Abweichungen von der Gesamtstichprobe. Diese waren meist auf die leicht unterschiedliche Zusammensetzung der Stichproben zurückzuführen. Aber auch Besonderheiten der Lernorte hatten dabei ein bedeutendes Gewicht.
Bezüglich der Lernbedingungen für die Lernorte ließen sich aus den Ergebnissen vor allem zwei Komponenten ermitteln: Zum einen die Architektur/räumliche Struktur der Lernorte. Hier können Faktoren wie drinnen/ draußen, Größe und die räumliche Orientierung unterschieden werden. All dies hat Auswirkungen auf das physische Wohlbefinden der Schüler, was wiederum eine Voraussetzung für eine hohe Lernmotivation ist. Die andere Hauptkomponente ist das am Lernort behandelte Thema. Hier kann grob zwischen Pflanzen und Tieren unterschieden werden. Pflanzen wurden dabei in mehreren Studien von den Schülern als weniger attraktiv eingeschätzt. Trotzdem sollten aber die Möglichkeiten, auch botanische Themen außerhalb der Schule zu behandeln, von den Lehrkräften zur Vermittlung biologischer Vielfalt genutzt werden.
Als Konsequenz der Ergebnisse kann der Besuch eines außerschulischen Lernrotes im Biologieunterricht bezüglich der Förderung der Lernmotivation unbedingt empfohlen werden. Da kein klarer Effekt des vor- und nachbereitenden Unterrichts der Biodiversitätsführungen erkennbar war, wären hier weitere Untersuchungen vonnöten, um genauere Aussagen machen zu können. Hier böten sich Studien mit Schülern anderer Altersgruppen und der Vergleich nur zweier außerschulischer Lernorte an.
Unter den weltweit in ständigem Gebrauch befindlichen Chemikalien befinden sich nicht nur Verbindungen mit akuter toxischer Wirkung, sondern auch solche mit Wirkung auf das endokrine System. Eine große Rolle spielt hier vor allem die Störung der Geschlechtsdifferenzierung und der Reproduktion, ausgelöst durch natürliche oder synthetische Chemikalien mit endokrinem Potential, sogenannte endokrine Disruptoren (ED). Diese Chemikalien können über unterschiedliche Eintragspfade in die Umwelt gelangen. Seit Mitte des 20. Jahrhunderts werden mehr und mehr Fälle bekannt, in denen anthropogene Chemikalien die Pflanzen- und Tierwelt belasten, darunter zahlreiche Befunde zu Störungen des Hormonsystems von Mensch und Tier.
Im Rahmen der Gefahren- und Risikobewertung steht bereits eine Vielzahl harmonisierter Prüfrichtlinien für die Identifizierung und Evaluierung der Effekte von (potentiellen) ED zur Verfügung. Um die Gesamtheit aller potentiellen Interaktionen von ED mit dem Hormonsystem detektieren zu können, ist die In-vivo-Untersuchung an Vertebraten in der Chemikalienregistrierung bisher unabdingbar. Bei der Untersuchung endokriner Potentiale in höheren Vertebraten spielen vor allem nager- und vogelbasierte Testsysteme eine wichtige Rolle. Diese bergen jedoch einen hohen zeitlichen, personellen und finanziellen Aufwand und erfordern eine massive Zahl an Versuchstieren, die für diese Tests benötigt werden. Darüber hinaus beinhalten Tierversuche eine Vielzahl von Problemen einschließlich ethischer Bedenken, die sich als Konsequenz der Tierhaltung unter Versuchsbedingungen ergeben. Ein sehr interessanter und vielversprechender Ansatz zur Reduktion von Tierversuchen ist die Entwicklung eines standardisierten Verfahrens für die Untersuchung potentieller ED in Vogelembryonen. Auf Vogelembryonen basierende In-ovo-Modelle stellen einen Mittelweg zwischen In-vitro- und In-vivo-Testsystemen dar. Mit dem Vogeleitest wird der sich entwickelnde Embryo, das für ED sensitivste Entwicklungsstadium im Leben eines Organismus, berücksichtigt.
Das Ziel der vorliegenden Arbeit war die Entwicklung und Eignungsuntersuchung eines auf dem Embryo des Haushuhns (Gallus gallus domesticus) basierenden Testsystems für den Nachweis von ED. Das resultierende Testsystem soll als Alternativmethode zu bisher etablierten nager- und vogelbasierten Testsystemen für die Untersuchung der Effekte hormonell aktiver Substanzen auf die Geschlechtsdifferenzierung in höheren Wirbeltieren eingesetzt werden.
Die im Rahmen der vorliegenden Dissertation durchgeführten Arbeiten umfassten sowohl die Charakterisierung der Normalentwicklung des Hühnerembryos, unbeeinflusst durch ED, als auch die morphologisch-histologischen Veränderungen der Gonaden von substanzexponierten Embryonen. Für die Untersuchung substanzbedingter Effekte, welche den Schwerpunkt der vorliegenden Arbeit darstellen, wurden die Embryonen gegenüber verschiedenen (anti)estrogenen und (anti)androgenen Substanzen exponiert. Unter Einfluss der Estrogene Bisphenol A (BPA) und 17α-Ethinylestradiol (EE2) entwickelten sich die Keimdrüsen der Männchen zu Ovotestes, während Weibchen ein Ovar mit deutlich schmalerem Cortex ausbildeten. Unter Einfluss der Antiestrogene Fulvestrant und Tamoxifen blieben Effekte auf die Gonaden männlicher Embryonen aus, eine durch das potente Estrogen EE2 hervorgerufene Feminisierung männlicher Gonaden konnte durch beide Substanzen jedoch effektiv antagonisiert werden. Weibchen bilden unter Einfluss von Tamoxifen deutlich schmalere linke Gonaden mit einem missgebildeten Cortex aus. Unter Einfluss der Androgene Tributylzinn (TBT) und 17α-Methyltestosteron (MT) blieben die Effekte auf männliche Embryonen aus, während die Weibchen anatomisch virilisierte Gonaden und eine Reduktion des linken gonadalen Cortex aufwiesen. Allein die untersuchten antiandrogenen Versuchssubstanzen Cyproteronacetat (CPA), Flutamid und p,p´-Dichlorodiphenyldichloroethen (p,p´-DDE) hatten keinen Effekt auf die gonadale Geschlechtsdifferenzierung männlicher und weiblicher Hühnerembryonen.
Es konnte gezeigt werden, dass der Embryo von G. gallus domesticus einen sensitiven Organismus innerhalb des Tierreichs darstellt und hinreichend sensitiv auf eine Reihe von endokrin wirksamen und reproduktionstoxischen Chemikalien reagiert. Anatomische und histologische Änderungen der Gonaden können daher als Biomarker für die Wirkung von ED bei Vögeln nützlich sein. Die untersuchten Endpunkte beziehen sich jedoch auf apikale Effekte und liefern keine mechanistischen Informationen zu den untersuchten Substanzen. Der
Hühnereitest ist eine sinnvolle Ergänzung zur bestehenden OECD-Testbatterie und zeichnet sich besonders durch seine kostengünstige und einfache Handhabung im Labor sowie einfach durchzuführende Tests aus. Durch die vergleichsweise kurze Versuchsdauer von nur 19 Tagen ist ein schnelles Substanzscreening möglich, welches zeitlich deutliche Vorteile gegenüber den etablierten nager- und vogelbasierten Testsystemen hat. Als Alternative zu bisherigen Assays könnte der vorgeschlagene Hühnereitest dazu beitragen, im Rahmen der (öko)toxikologischen Gefährdungs- und Risikobewertung von Chemikalien künftig weniger Versuchstiere zu verwenden.
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.
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.
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...