Biologische Hochschulschriften (Goethe-Universität; nur lokal zugänglich)
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Succinate:quinone oxidoreductases (SQORs) are integral membrane protein complexes, which couple the two-electron oxidation of succinate to fumarate (succinate → fumarate + 2H+ + 2e-) to the two-electron reduction of quinone to quinol (quinone + 2H+ + 2e- → quinol) as well as catalyzing the opposite reaction, the reduction of fumarate by quinol. In mitochondria and some aerobic bacteria, succinate:ubiquinone reductase, also known as complex II of the aerobic respiratory chain or as succinate dehydrogenase from the tricarboxylic acid (TCA or Krebs) cycle, catalyzes the oxidation of succinate by ubiquinone, which is mildly exergonic under standart conditions and not directly associated with energy storage in the form of a transmembrane electrochemical proton potential (Δp). Gram-positive bacteria do not contain ubiquinone but rather menaquinone, a quinone with significantly lower oxidation-reduction (“redox”) midpoint potential. In these cases, the catalyzed oxidation of succinate by quinone is endergonic under standard conditions. Consequently, these bacteria face a thermodynamic problem in supporting the catalysis of this reaction in vivo. Based on experimental evidence obtained on whole cells and purified membranes, it had previously been proposed that the SQR from Gram-positive bacteria supports this reaction at the expense of the protonmotive force, Δp. Nonetheless, it has been argued that the observed Δp dependence is not associated specifically with the activity of SQR because the occurrence of artifacts in experiments with bacterial membranes and whole cells can not be fully excluded. Clearly, definitive insight into the mechanism of catalysis of this intriguing reaction required a corresponding functional characterization of an isolated, membranebound SQR from a Gram-positive bacterium. The first aim of the present work addresses the question if the general feasibility of the energetically uphill electron transfer from succinate to menaquinone is associated specifically to a single enzyme complex, the SQR. The prerequisite to achieve this goal was stable preparation of this enzyme.
LmrA is a member of the ATP Binding Cassette (ABC) transporter family of membrane proteins and a structural and functional homologue of P-glycoprotein1, 2. ABC-transporters share a common architecture of two transmembrane domains and two nucleotide binding domains. The NBDs are highly conserved in this transporter family whereas the TMDs are highly diverse3. The TMDs recognize the substrate and the NBDs bind and hydrolyze ATP and thus contribute the energy for substrate translocation. ABC transporters as a protein family transport a high number of substrates including peptides, nutrients, ions, bile acids, lipids and other lipophilic compounds. LmrA is a multidrug transporter that recognizes a number of hydrophobic substrates including fluorescent dyes and antibiotics1, 4-6. LmrA is a native protein of the gram-positive bacterium Lactococcus lactis. In this thesis, L. lactis was used as a homologous expression host for the preparation of LmrA for a variety of experiments. Wildtype LmrA as well as a number of cysteine mutants were successfully expressed in L. lactis, purified and subsequently characterized by a variety of biochemical assays (Chapter 4). LmrA can be expressed to very high amounts in L. lactis. The purification and reconstitution were optimized for the requirements of solid-state NMR experiments in this thesis. For the first time, an ABC transporter has been reconstituted in synthetic lipids to a ratio of up to 1:150 (mol/mol). LmrA was shown to be active under magic angle spinning conditions with these reconstitution ratios. By taking advantage of the slower ATP hydrolysis by LmrA ΔK388 (lysine deletion in the Walker A motif), a real-time 31P solid-state NMR ATPase assay was established (Chapter 5). This assay allowed, for the first time, the investigation of all phosphor nuclei during the ATP hydrolysis cycle of a membrane protein simultaneously and in real time7. This assay has been successfully adapted to investigate both ATP hydrolysis and substrate phosphorylation of diacylglycerol kinase (together with S. Wollschlag) and ATP hydrolysis at high temperatures of the thermophilic ABC transporter ABC1 from Thermos thermophilus (together with A. Zutz). In the course of this thesis, the gene for LmrA has been cloned into expression vectors suitable for Escherichia coli and the heterologous expression of LmrA was established (Chapter 4). The functionality of the heterologously expressed protein has been investigated and compared to L. lactis LmrA. In these experiments, LmrA was shown to yield a distinct multidrug resistance phenotype in its E. coli host and to show secondary active multidrug transport in the absence of ATP and presence of a proton gradient [Hellmich et al, in prep] (Chapter 4). Previously, it had been shown that LmrA acts as a seconadary active transporter when the NBDs are truncated8. The overexpression in minimal and defined medium and the purification of LmrA from E. coli have been optimized. Isotope labeling for ssNMR has been established and the first multinuclear ssNMR experiments have been carried out on a functional ABC transporter (Chapter 8). ABC transporters couple two cycles: upon ATP binding, the NBDs dimerize, hydrolyze the ATP, subsequently release Pi and ADP and finally dissociate. During this cycle, conformational changes are relayed to the TMDs which utilize the energy from ATP binding and/or hydrolysis to translocate the respective substrate. The prehydrolysis state can be trapped by beryllium fluoride, whereas the post-hydrolysis state of this cycle can be trapped by vanadate9-12. Trapping protocols for these reagents were successfully established for LmrA in this thesis (Chapter 4). This allowed for the investigation of different catalytic states by both ssNMR and EPR. A general 19F labeling protocol for membrane proteins has been established in the course of this thesis and successfully applied to proteorhodopsin (together with N. Pfleger)13 and LmrA (chapter 6). Single cysteine mutants of LmrA that line out the dimer interface have been labeled with a fluorine label for ssNMR. In the apo state, the 19F labeling indicates highly flexible transmembrane domains, a finding that is supported by 13C ssNMR and EPR measurements. The addition of drugs has a different effect on different positions within the LmrA dimer, therefore indicating that different drugs are recognized at a different position within the protein. For P-glycoprotein and LmrA it has been previously shown by biochemical methods that different drug binding sites co-exist. For a 19F label attached at position 314 (LmrA E314C), the spectra showed two distinct peaks with similar populations. This could hint towards a structural asymmetry within the LmrA dimer that might also be reflected in the alternating ATP hydrolysis at the NBDs. E314 has been specifically implicated with drug transport. Thus, structural asymmetry at this position might be functionally relevant for guiding a substrate through the transporter. Structural asymmetry within a homodimeric ABC transporter has also been shown for BtuCD, the E. coli vitamin B12 importer14. In addition, the conserved glutamates in EmrE, a small multidrug resistance protein, were shown to be asymmetric in the drug bound state15. Both, uniformly 13C/15N labeled as well as selectively amino acid type labeled LmrA has been investigated in different conformational states. Interestingly, significant dynamic changes in the b-sheet regions of LmrA (confined to the NBDs) were observed in the pre-hydrolysis (beryllium fluoride) and transition state (vanadate trapped) state. These were interpreted as the transition from a domain in fast conformational exchange in the apo state to one of intermediate exchange in the nucleotide bound state. A significant change in NBD mobility upon nucleotide binding was previously also shown with 2H ssNMR on LmrA16. By EPR it was shown that LmrA in both the vanadate and BeFx trapped states displays a significantly higher rigidity and therefore defined distances, whereas the apo state resembled a “floppy” protein with no preferred distance distribution. This concurs with data obtained from 19F ssNMR with fluorine labeled single-cysteine mutants. Here, in agreement with the EPR data, a higher label (and possibly) protein mobility was observed in the apo state displaying rather broad line widths. Upon trapping with vanadate, the line widths of the majority of fluorine-labeled mutants decreased due to an enhanced protein rigidity and a more homogenous environment of the fluorine labels. A similar observation was made when increasing the temperature that can be explained due to higher protein flexibility at increased temperatures. Solution NMR was employed to investigate the isolated soluble NBD of LmrA (Chapter 9). First 2D and 3D spectra were successfully obtained and could be utilized for a preliminary assignment of a significant fraction of residues. Additionally, binding of ATP and ADP in absence and presence of magnesium was investigated. Finally, the effects of peptides emulating the coupling helices of the full-length transporter on the soluble NBD were investigated. Strikingly, binding of one of these peptides only occurred in the presence of nucleotides (whereas the other showed no binding at all) hinting towards a tightly coupled regulation of the NBD and TMD during the substrate translocation/ATP hydrolysis cycle based on nucleotide binding.
ß1-integrins are essential for angiogenesis but the mechanisms regulating integrin function in endothelial cells (EC) and their contribution to angiogenesis remain elusive. BRAG2 is a guanine nucleotide exchange factor for the small Arf-GTPases Arf5 and Arf6. The role of BRAG2 in EC and angiogenesis and the underlying molecular mechanisms remains unclear. siRNA-mediated BRAG2-silencing reduced EC angiogenic sprouting and migration. BRAG2-siRNA-transfection differentially affected a5ß1- and aVß3-integrin function: specifically, BRAG2-silencing increased focal/fibrillar adhesions and EC adhesion on ß1-integrin-ligands (fibronectin and collagen), while reducing the adhesion on the aVß3-integrin-ligand, vitronectin. Consistent with these results, BRAG2-silencing enhanced surface expression of a5ß1-integrin, while reducing surface expression of aVß3-integrin. Mechanistically, BRAG2 mediated recycling of aVß3-integrins and endocytosis of ß1-integrins and specifically of the active/matrix bound a5ß1-integrin present in fibrillar/focal adhesions (FA), suggesting that BRAG2 contributes to the disassembly of FA via ß1-integrin-endocytosis. Arf5 and Arf6 are promoting downstream of BRAG2 angiogenic sprouting, ß1-integrin-endocytosis and the regulation of FA. In vivo silencing of the BRAG2-orthologues in zebrafish embryos using morpholinos perturbed vascular development. Furthermore, in vivo intravitral injection of plasmids containing BRAG2-shRNA reduced pathological ischemia-induced retinal and choroidal neovascularization. These data reveals that BRAG2 is essential for developmental and pathological angiogenesis by promoting EC sprouting through regulation of adhesion by mediating ß1-integrin internalization and associates for the first time the process of ß1-integrin endocytosis with angiogenesis.
The canonical Wnt/β-catenin and the Shh pathway as well as the Notch signaling cascade
are key regulators in stem cell biology and are independently associated with the development
of cancer. Despite the knowledge of a balanced signaling for cellular maintenance, the
fundamental biochemical mechanisms of crosstalk are still poorly understood. This study
demonstrates that the outcome of interaction between Wnt and Shh is cell type specific. A
combined inhibitory mechanism of the Shh and Notch2/Jagged2 pathways on dominant
active β-catenin signaling in the adult tongue epithelium keeps Wnt/β-catenin signaling
restricted to physiological tolerable levels. In the opposite crosstalk the activation of
Wnt/β-catenin signaling in medulloblastoma (MB) of the Shh subtype, in turn inhibits the Hh
pathway.
The inhibitory mechanism of Shh and Notch2/Jagged2 on Wnt/β-catenin signaling is
independent of the degradation complex of β-catenin and takes place inside the nucleus.
Furthermore, the negative feedback on Wnt/β-catenin signaling by the Shh pathway relies
on transcriptional activity of Gli1/2A. Inhibition of Gli1/2A with the specific inhibitor GANT61
abrogated the negative impact of Shh on β-catenin signaling in vitro. Although the negative
feedback loop of Shh is still functional in human SCC25 cells, the inhibitory effect of
Notch2/Jagged2 is lost and contributes to the cancerogenic phenotype of these cells. In the
inverse situation, the activation of β−catenin signaling has a negative feedback on
constantly active Shh signaling and significantly inhibits the Hh pathway. This was shown in
Ptch+/- and Math1-Cre:SmoM2Fl/+ MB tumor spheres in vitro, in which inhibition of sphere
formation and growth was observed and Hh target gene transcription was down-regulated.
This demonstrates for the first time that the activation of canonical Wnt/β-catenin signaling
in primary MB cells with a Hh pathway over-activation has a negative effect on the growth of
these cells in vitro.
In summary the results show that crosstalk of Wnt/β-catenin and Shh signaling has context
specific outcome on pathway activity. Elucidation of the molecular interactions will improve
our understanding of Wnt and Hh associated tumors and contribute to the development of
new therapeutic strategies.
Orthopoxviruses are large DNA viruses that replicate within the cytoplasm of infected cells encoding over a hundred different proteins. The orthopoxviral 68k ankyrin‐like protein (68k‐ank) is highly conserved among orthopoxviruses, and this study aimed at elucidating the function of 68k‐ank. The 68k‐ank protein is composed of four ankyrin repeats (ANK) and an F‐box‐like domain; both motifs are known proteinprotein interaction domains. The F‐box is found in cellular F‐box proteins (FBP), crucial components of cellular E3 ubiquitin (Ub) ligases. With yeast‐two‐hybrid screens and subsequent co‐immunoprecipitation analyses, it was possible to identify S‐phase kinase‐associated protein 1a (Skp1a) as a cellular counterpart of 68k‐ank via binding to the F‐box‐like domain. Additionally, Cullin‐1 was co‐precipitated, suggesting the formation of a viral‐cellular SCF E3 Ub ligase complex. Modified Vaccinia virus Ankara (MVA) ‐ being attenuated and unable to replicate in most mammalian cell lines due to a block in morphogenesis – nevertheless, expresses its complete genetic information attributing to its properties as promising vector vaccine. Conservation of 68k‐ank as the only ANK protein encoded by MVA implied a substantial role of this viral factor. Hence, its function in the viral life cycle was assessed by studying a 68k‐ank knock‐out MVA. A mutant phenotype manifested in nonpermissive mammalian cells characterized by a block succeeding viral early gene expression and by a reduced ability of the virus to shutoff host protein synthesis. Studies with MVA encoding a 68k‐ank F‐box‐like domain truncated protein revealed that viral‐cellular SCF complex formation and maintenance of viral gene expression are two distinct, unrelated functions fulfilled by 68k‐ank. Moreover, K1, a well‐described VACV host range factor of the ANK protein family, is able to complement 68k‐ank function. This suggests that gene expression of MVA putatively depends on the ANKs encoded in 68k‐ank. In addition to the important findings in vitro, first virulence studies with the mouse pox agent, ectromelia virus (ECTV) deleted of the 68k‐ank ortholog (C11) suggested that this factor contributes to ECTV virulence in vivo.
The importance of RNA in molecular and cell biology has long been underestimated. Besides transmitting genetic information, studies of recent years have revealed crucial tasks of RNA especially in gene regulation. Riboswitches are natural RNA-based genetic switches and known only for ten years. They directly sense small-molecule metabolites and regulate in response the expression of the corresponding metabolic genes. Within recent years, artificial riboswitches have been developed that operate according to user-defined demands. Hence, they represent powerful tools for synthetic biology.
This study focused on the development of engineered catalytic riboswitches for conditional gene expression in eukaryotes. A self-cleaving hammerhead ribozyme was linked to a tetracycline binding aptamer in order to regulate ribozyme cleavage allosterically with tetracycline. By integrating such a hybrid molecule into a gene of interest, mRNA cleavage and thereby gene expression is controllable in a ligand dependent manner. The linking domain between ribozyme and aptamer was randomised. Tetracycline inducible ribozymes were isolated after eleven cycles of in vitro selection (SELEX). 80% of the analysed ribozymes show cleavage that strongly depends on tetracycline. In the presence of 1 μM tetracycline, their cleavage rates are comparable to that of the parental hammerhead ribozyme. In the absence of tetracycline, cleavage rates are inhibited up to 333-fold. The allosteric ribozymes bind tetracycline with similar affinity and specificity as the parental aptamer. Ribozyme cleavage is fully induced within minutes after addition of tetracycline. Interestingly, the isolated linker domains exhibit structural consensus motives rather than consensus sequences.
When transferred to yeast, three switches reduced reporter gene expression by 30 - 60% in the presence of tetracycline; none of them controlled gene expression in mammalian cells. In vitro selected molecules do not necessarily retain their characteristics when applied in a cellular context. Therefore, high throughput screening and selection systems have been developed in mammalian cells. The screening system is based on two fluorescent reporter proteins (GFP and mCherry). 1152 individual constructs of the selected ribozyme pool were tested, but none of them reduced reporter gene expression significantly in the presence of tetracycline. The selection system employs a fusion peptide encoding two selection markers (Hygromycin B phosphotransferase and HSV thymidine kinase) facilitating both negative and positive selection. 6.5 x 104 individual constructs of the selected ribozyme pool are currently under investigation.
The biogenesis and function of photosynthetically active chloroplasts relies on the import of thousands of nuclear encoded proteins via the coordinated actions of two multiprotein translocon machineries in the outer and inner envelope membrane. Trafficking of preproteins across the soluble compartment of InterMembrane Space (IMS) is currently envisioned to be facilitated by an IMS complex composed of outer envelope proteins Toc64 and Toc12, a soluble IMS component, Tic22 and an IMS-localized Hsp70. Among them, currently Tic22 is the only component that stands undisputed in terms of its existence. Having two closely related homologs in A. thaliana, their biochemical and functional characterization was still lacking. A critical analysis of Tic22 knockout mutants displayed growth phenotype reminiscent of ppi1, the mutant of Toc33. However, both the genes have similar expression patterns with no clear preference for photosynthetic or nonphotosynthetic tissues, which explained the absence of a detectable phenotype in single mutants. In addition, transgenic complementation study with either of the homolog affirmed the identical localization of both proteins in the IMS which characterizes the two homologs as functionally redundant. Based on the pale-yellow phenotype exhibited by the double mutant plants, an attempt to analyze the import capacity of a stromal substrate in the double mutant revealed threefold reduction when compared to wild-type acknowledging the essential role of Tic22 in the import mechanism. Initially, Tic22 was identified together with another protein, Tic20, which has been heavily discussed as a protein conducting channel in the inner membrane. Despite being characterized, in A. thaliana, two out of four homologs of Tic20 are differentially localized with one being additionally localized in mitochondria and the other, exclusively residing in the thylakoids.
According to in silico analysis, for all the Tic20 proteins, a four-helix transmembrane topology was predicted. Accordingly, its topology was mapped by employing the recently established selfassembling GFP-based in vivo experiments. Astonishingly, the expression of one of the inner envelope localized Tic20 homolog enforces inner membrane proliferation affecting the shape and organization of the membrane. Therefore this study focuses on analyzing the effects of high envelope protein concentrations on membrane structures, which together with the existing results, an imbalance in the lipid to protein ratio and a possible role of signaling pathway regulating membrane biogenesis is discussed.
Drug toxicity and viral resistance limit long-term efficacy of antiviral drug treatment for HIV
infection. Thus, alternative therapies need to be explored. Previously, group of “Prof. von Laer”
tested the infusion of T lymphocytes transduced with a retroviral vector (M87o) that expresses an
HIV entry inhibitory peptide (maC46). Gene-modified autologous T cells were infused into 10
HIV-infected patients with advanced disease and multidrug resistant virus during antiretroviral
combination therapy. T cell infusions were tolerated well with no severe side effects. A
significant increase of CD4 counts was observed post infusion. At the end of the one-year
follow-up, the CD4 counts of all patients were still around or above baseline. Gene-modified
cells could be detected in peripheral blood, lymph nodes and bone marrow throughout the oneyear
follow-up, whereby marking levels correlated with the cell dose. No significant changes of
viral load were observed during the first four months. Four of the seven patients that changed
their antiviral drug regimen thereafter responded with a significant decline in plasma viral load.
In conclusion, the transfer of gene-modified cells was safe, led to sustained levels of gene
marking and may improve immune competence in HIV-infected patients with advanced disease
and multidrug resistant virus. However, the low level of gene marking and the lack of substantial
long-term in vivo accumulation of gene-protected cells observed in this trial clearly demonstrate
the requirement for new vectors with new strategy.
In this thesis self‐inactivating lentiviral vectors harboring internal promoters and RNA elements
were therefore evaluated for their potential use in a clinical gene‐therapy trial. The results from
this work provide the basis for the selection of a suitable candidate vector for extensive
preclinical testing. Apart from being capable of transducing non‐dividing cells, lentiviral vectors
incorporate a number of additional features that are of potential value for gene therapeutic
applications. These include a larger packaging capacity, higher titers than γ‐retroviral vectors
and, most importantly, a reduced risk of deregulating cellular genes due to its natural integration
profile. The use of internal promoters to drive expression of the therapeutic transgene maC46
should further improve the safety profile of these new‐generation vectors, while an additional
artificial splice acceptor (SA) into the 5‟UTR of the transgene over all elevate transgene
expression. The rationale for this is that hematopoietic stem and progenitor cells will be
Summary
98
protected from enhancer‐mediated transactivation effects and also from potential side effects due
to the aberrant expression of maC46 while at the same time the full clinical benefit for the
patients is maintained.
In order to find a suitable candidate for preclinical studies, two candidate therapeutic vectors
harboring different regulatory elements were selected based on results from pilot experiments.
The internal promoters used to drive expression of codon optimized maC46 were the PGK
promoter and MPSV promoter. This work focuses on the transgene expression levels in
lymphoid cells and antiviral activity. The issues of long term expression, propensity to
methylation mediated silencing of the promoters, and genotoxicity were also touched. In a first
step the performance of different vectors was evaluated in the human T cell lines. Based on
promising data from ex vivo human peripheral blood mononuclear cells, the vector carrying the
MPSV promoter along with intron were selected for in vivo transplantation experiments.
In summary, the ex vivo data suggested the long term survival of lentiviral gene modified cells,
along with maintained expression of introduced genes. It was observed that the expression of
these constructs depends strongly on the activation and differentiation status of the targeted T
cells. This regulation was not linked to any specific promotor. In vivo study shows that maC46
can be introduced into murine multiple hematopoietic lineages via lentiviral vector and expressed
at high levels in their mulilineage progeny, without altering the hematopoiesis. There was no
sign of any kind of hematopoietic or lymphoid malignancies. Although gene-modified
lymphocytes persisted in-vivo, the downregulation of transgene expression was consistent with
the ex-vivo observation. In contrast to that the T cells transplanted group showed delayed
engraftment of donor cells and there was no expression of C46 in blood and lymphatic organs. .
In conclusion, when considering HIV gene therapy focusing CD4+ T cells, potential problems of
T cell activation status as related to the desired clinical effect must be addressed. These results
might open the way for a gene therapy targeting mainly or exclusively activated T cells and
could be exploited for immunostimulatory as well as suppressive approaches.
Wastewater treatment plants (WWTPs) do not eliminate micropollutants completely and are thus important point sources for these substances. In particular, concerns about en-docrine disrupting compounds in WWTP effluents give rise to the implementation of advanced treatment steps for the elimination of trace organic contaminants. The present study investigated ozonation (O3) and activated carbon treatment (AC) at two WWTPs. For an ecotoxicological assessment at WWTP Regensdorf, conventionally treated wastewater, wastewater after ozonation, and ozonated wastewater after sand filtration were evaluated in parallel via the fish early life stage toxicity test (FELST) using rainbow trout (Oncorhynchus mykiss). Additionally, a comparative toxicity evalu-ation of ozonated and activated carbon treated effluents was performed at the pilot scale treatment plant in Neuss (WWTP Neuss). For this purpose, four invertebrate tests and one higher plant toxicity test were selected to assess potential biological effects on or-ganisms [Lemna minor growth inhibition test, chironomid toxicity test with Chironomus riparius, Lumbriculus variegatus toxicity test, comet assay with haemolymph of the zebra mussel (Dreissena polymorpha), reproduction test with Potamopyrgus antipo-darum]. All in vivo assays were performed on site at the treatment plants in flow-through test systems. Furthermore, the present study investigated the effects of ozona-tion and activated carbon treatment on endocrine activities [estrogenicity, anti-estrogenicity, androgenicity, anti-androgenicity, aryl-hydrocarbon receptor (AhR) agonistic activity] with yeast based bioassays using solid phase extracted water samples. To evaluate the removal of in vitro non-specific toxicity, a cytotoxicity assay using a rat cell line was applied. The FELST at WWTP Regensdorf revealed a considerable developmental retardation of test organisms exposed to ozonated WW. This was accompanied by a significant decrease in body weight and length compared to reference water, to the conventionally treated WW, and to the ozonated water after sand filtration. Hence sand filtration obvi-ously prevents from adverse ecotoxicological effects of ozonation. An additional test – starting with yolk-sac larvae – resulted in a significant reduction of vitellogenin levels in fish exposed to ozonated wastewater compared to fish reared in conventionally treat-ed wastewater. This demonstrates the effective removal of estrogenic activity by ozonation. At WWTP Neuss, the reproduction test with the mudsnail P. antipodarum exhibited a decreased reproductive output after advanced treatment compared to conventional treatment. This indicates an effective estrogenicity removal by ozonation and activated carbon treatment and is confirmed by results of the yeast estrogen screen with a reduc-tion of in vitro estrogenic activity by > 75%. The L. variegatus test revealed a signifi-cantly enhanced toxicity after ozonation compared to conventional treatment, whereas this effect was reduced following subsequent sand filtration. When ozonation was applied, a significantly increased genotoxicity was observed, detected with the comet assay using haemolymph of the zebra mussel. Again, this effect was removed by subsequent sand filtration to the level of conventional treatment. Activated carbon treatment even resulted in a significant reduction of genotoxicity. At both treatment plants, adverse effects after ozonation may have been a result of the formation of toxic oxidation by-products. However, sand filtration reduced toxication effects, indicating that these oxidation by-products are readily degradable or adsorbable. The results point out that, in any case, ozonation should not be applied without subsequent biologically active post treatment appropriate for oxidation by-products removal (e.g. sand filtration). However, only activated carbon achieved a toxicity reduction compared to the conventional treated wastewater. Thus, it cannot be excluded that po-tential beneficial effects due to ozonation might be masked by residual toxic oxidation by-products passing the sand filter or ozonation is not as effective in toxicity removal as PAC treatment. The yeast based assays with solid phase extracted samples revealed an effective endo-crine activity removal during ozonation and activated carbon filtration (estrogenicity: 77 – 99%, anti-androgenicity: 63 – 96%, AhR agonistic activity: 79 – 82%). The cyto-toxicity assay exhibited a 32% removal of non-specific toxicity after ozonation com-pared to conventional treatment. Ozonation in combination with sand filtration reduced cytotoxic effects by 49%, indicating that sand filtration contributes to the removal of toxicants. Activated carbon treatment was the most effective technology for cytotoxici-ty removal (61%). Sample evaporation reduced cytotoxic effects by 52% (after activated carbon treatment) to 73% (after ozonation), demonstrating that volatile substances contribute considerably to toxic effects, particularly after ozone treatment. These results confirm an effective removal or transformation of toxicants with receptor mediated mode of action and non-specific toxicants during both investigated treatment steps. However, due to the limited extractability, polar ozonation by-products were neglected for toxicity analysis, and hence non-specific toxicity after O3 is underestimated. In the long run, only on-site comparisons at WW receiving water bodies (e.g. communi-ty analysis of fish, macroinvertebrates, plants, microorganisms) – before and after up-grading WWTPs – allow drawing environmentally relevant conclusions regarding bene-fits and risks of advanced WW treatment methods. Conclusively, the benefits and possible negative impacts have to be carefully evaluated to prove that not more environmental impact will be induced than removed by advanced treatment technologies as each additional treatment requires considerable amounts of energy, resources, and infrastructure facilities. Accordingly, comprehensive sustainable approaches for pollution prevention and wastewater treatment (e.g. source control and source separation) are preferable compared to end-of-pipe treatment systems.
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.