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Heat exchangers are used for thickening of various products or desalination of saltwater. Nevertheless, they are used as cooling unit in industries. Thereby, the stainless steel heat transferring elements get in contact with microorganism containing media, such as river water or saltwater, and corrode. After at least two years of utilization the material is covered with bacterial slime called biofilm. This process is called biofouling and causes loss in efficiency and creates huge costs depending on cleaning technique and efficiency. Cleaning a heat exchanger is very expensive and time consuming. It only can be done while the device is out of business.
Changing the surface properties of materials is the best and easiest way to lengthen the initial phase of biofilm formation. This leads to less biofouling (Mogha et al. 2014).
Thin polymer films as novel materials have less costs in production than stainless steel and are easy to handle. Furthermore, they can be functionalzed easily and can be bougth in different sizes all over the world. Because of this, they can reduce the costs of cleaning techniques and lead to a longer high efficiency state of the heat exchanger. If the efficiency of the heat exchanger decreases, the thin polymer films can be replaced.
For a successful investigation of the microbial and the process engineering challenges a cooperation of Technical University of Kaiserslautern (chair of seperation science and technology) and University of Koblenz-Landau (working goup microbiology) was established.
The aim of this work was design engineering and production of a reactor for investigation of biofouling taking place on thin polymeric films and stainless steel. Furthermore, an experimental design has to be established. Several requirements have to be applied for these tasks. Therefore, a real heat exchanger is downscaled, so the process parameters are at least comparable. There are many commercial flow cell kits available. Reducing the costs by selfassembling increased the number of samples, so there is a basis for statistic analysis. In addition, fast and minimal invasive online-in-situ microscopy and Raman spectroscopy can be performed. By creating laminary flow and using a weir we implemented homogenous inflow to the reactors. Reproduceable data on biomass and cell number were created.
The assessment of biomass and cell number is well established for drinking water analysis. Epifluorescense microscopy and gravimetric determination are the basic techniques for this work, too. Differences in cell number and biomass between surface modifications and materials are quantified and statistically analysed.
The wildtype strain Escherichia coli K12 and an inoculum of 500 ml fresh water were used to describe the biofouling of the films. Thereby, we generated data with natural bacterial community in unknown media properties and data with well known media properties, so the technical relevance of the data is given.
Free surface energy and surface roughness are the first attachment hurdles for bacteria. These parameters were measured according to DIN 55660 and DIN EN ISO 4287. The materials science data were correlated with the number of cells and the biomass. This correlation acts as basal link of biofouling as biological induced parameter to the material properties. Material properties for reducing the biofouling can be prospected.
By using Raman spectroscopy as a cutting edge method future investigations could be shortened. If biomass or cell number can be linked with the spectra, new functional materials can be investigated in a short time.
SUMMARY
Buildings and infrastructures characterize the appearance of our cultural landscapes and provide essential services for the human society. However, they inevitably impact the natural environment e.g. by the structural change of habitats. Additionally, they potentially cause further negative environmental impacts due to the release of chemical substances from construction materials. Galvanic anodes and organic coatings regularly used for corrosion protection of steel structures are building materials of particular importance for the transport infrastructure. In direct contact with a water body or indirectly via the runoff after rainfall, numerous chemicals can be released into the environment and pose a risk to aquatic organisms. Up to now, there is no uniform investigation and evaluation approach for the assessment of the environmental compatibility of building products. Furthermore, galvanic anodes and organic coatings pose particular challenges for their ecotoxicological characterization due to their composition. Therefore, the objective of the presented thesis was the ecotoxicological assessment of emissions from galvanic anodes and protective coatings as well as the development of standardized assessment procedures for these materials.
The possible environmental hazard posed by the use of anodes on offshore installations was investigated on three trophic levels. To ensure a realistic and reliable evaluation, the experiments were carried out in natural seawater and under natural pH conditions. Moreover, the anode material and its main components zinc and aluminum were exposed while simulating a worst-case scenario. The anode material examined caused a weak inhibition of algae growth; no acute toxicity was observed on the luminescent bacteria and amphipods. However, an increase of aluminum and indium levels in the crustacean species was found. On the basis of these results, no direct threat has been identified for marine organisms from the use of galvanic aluminum anodes. However, an accumulation of metals in crustaceans and a resulting entry into the marine food web cannot be excluded.
The environmental compatibility of organic coating systems was exemplarily evaluated using a selection of relevant products based on epoxy resins (EP) and polyurethanes. For this purpose, coated test plates were dynamically leached over 64 days. The eluates obtained were systematically analyzed for their ecotoxicological effects (acute toxicity to algae and luminescent bacteria, mutagenic and estrogenic effects) and their chemical composition. In particular, the EP-based coatings caused significant bacterial toxicity and estrogen-like effects. The continuously released 4-tert-butylphenol was identified as a main contributor to these effects and was quantified in concentrations exceeding the predicted no effect concentration for freshwater in all samples. Interestingly, the overall toxicity was not governed by the content of 4-tert-butylphenol in the products but rather by the release mechanism of this compound from the investigated polymers. This finding indicates that an optimization of the composition can result in the reduction of emissions and thus of environmental impacts - possibly due to a better polymerization of the compounds.
Coatings for corrosion protection are exposed to rain, changes in temperature and sun light leading to a weathering of the polymer. To determine the influence of light-induced aging on the ecotoxicity of top coatings, the emissions and associated adverse effects of UV-irradiated and untreated EP-based products were compared. To that end, the investigation of static leachates was focused on estrogenicity and bacterial toxicity, which were detected in the classic microtiter plate format and in combination with thin-layer plates. Both materials examined showed a significant decrease of the ecotoxicological effects after irradiation with a simultaneous reduction of the 4-tert-butylphenol emission. However, bisphenol A and various structural analogues were detected as photolytic degradation products of the polymers, which also contributed to the observed effects. In this context, the identification of bioactive compounds was supported by the successful combination of in-vitro bioassays with chemical analysis by means of an effect-directed analysis. The presented findings provide important information to assess the general suitability of top coatings based on epoxy resins.
Within the scope of the present study, an investigation concept was developed and successfully applied to a selection of relevant construction materials. The adaptation of single standard methods allowed an individual evaluation of these products. At the same time, the suitability of the ecotoxicological methods used for the investigation of materials of unknown and complex composition was confirmed and the basis for a systematic assessment of the environmental compatibility of corrosion protection products was created. Against the background of the European Construction Products Regulation, the chosen approach can facilitate the selection of environmentally friendly products and contributes to the optimization of individual formulations by the simple comparison of different building materials e.g. within a product group.
Because silver nanoparticles (Ag NPs) are broadly applied in consumer products, their leaching will result in the continuous release of Ag NPs into the natural aquatic environment. Therefore, bacterial biofilms, as the prominent life form of microorganisms in the aquatic environment, are most likely confronted with Ag NPs as a pollutant stressor. Notwithstanding the significant ecological relevance of bacterial biofilms in aquatic systems, and though Ag NPs are expected to accumulate within these biofilms in the environment, the knowledge on the environmental and ecological impact of Ag NPs, is still lagging behind the industrial growth of nanotechnology. Consequently, aim of this thesis was to perform effect assessment of Ag NP exposure on bacterial biofilms with ambient Ag NPs concentrations and under environmentally relevant conditions. Therefore, a comprehensive set of methods was applied in this work to study if and how Ag NPs of two different sizes (30 and 70 nm) affect bacterial biofilms i.e. both monospecies biofilms and freshwater biofilms in environmentally relevant concentrations (600 - 2400 µg l-1). Within the first part of this work, a newly developed assay to test the mechanical stability of
monospecies biofilms of the freshwater model bacterium Aquabacterium citratiphilum was validated. In the first study, to investigate the impact of Ag NPs on the mechanical stability of bacterial biofilms, sublethal effects on the mechanical stability of the biofilms were observed with negative implications for biostabilization. Furthermore, as it is still challenging to monitor the ecotoxicity of Ag NPs in natural freshwater environments, a mesocosm study was performed in this work to provide the possibility for the detailed investigation of effects of Ag NPs on freshwater biofilms under realistic environmental conditions. By applying several approaches to analyze biofilms as a whole in response to Ag NP treatment, insights into the resilience of bacterial freshwater biofilms were obtained. However, as revealed by t-RFLP fingerprinting combined with phylogenetic studies based on the 16S gene, a shift in the bacterial community composition, where Ag NP-sensitive bacteria were replaced by more Ag NP-tolerant species with enhanced adaptability towards Ag NP stress was determined. This shift within the bacterial community may be associated with potential detrimental effects on the functioning of these biofilms with respect to nutrient loads, transformation and/or degradation of pollutants, and biostabilization. Overall, bringing together the key findings of this thesis, 4 general effect mechanisms of Ag NP treatment have been identified, which can be extrapolated to natural freshwater biofilms i.e. (i) the identification of Comamonadaceae as Ag NP-tolerant, (ii) a particular resilient behaviour of the biofilms, (iii) the two applied size fractions of Ag NPs exhibited similar effects independent of their sizes and their synthesis method, and (iv) bacterial biofilms show a high uptake capacity for Ag NPs, which indicates cumulative enrichment.
The presence of synthetic chemicals in the environment can affect both ecosystems and
human health. In particular, the increasing contamination of the aquatic environment by
complex mixtures of anthropogenic trace substances has become a major global concern.
Once released into the environment, these compounds can undergo diverse
transformation processes to form a wide range of transformation products (TPs), which
are commonly unknown. Transformation inevitably alters the pattern of contamination and
exposure, as new substances are formed with frequently different physicochemical
properties, environmental behavior and toxicity in comparison to their precursor
compounds. For instance, TPs can exhibit significantly greater persistence and mobility in
the aquatic environment, posing a threat to both aquatic ecosystems and drinking water
resources. Therefore, TPs need to be considered in the risk assessment and authorization
process of chemicals. However, due to a combination of predictive, analytical, and
regulatory challenges, TPs currently remain largely unrecognized and unregulated. By
addressing these challenges, this thesis comprehensively characterizes the entry paths,
occurrence, fate, and (eco)toxicological relevance of selected TPs in the aquatic system in
Germany. These TPs have been largely overlooked in environmental studies and aquatic
monitoring programs for decades, despite their precursors being produced and used in
large quantities on a global scale.
The highly persistent and mobile substance trifluoroacetate (TFA) has garnered
significant attention in recent years due to its diverse sources, widespread occurrence in
the aquatic environment, and the lack of economically viable options to remove TFA from
contaminated waters. One of the most frequently discussed diffuse sources is the
formation of TFA in the atmosphere through the oxidation of volatile precursors and its
subsequent scavenging from the atmosphere by wet deposition. Despite the previously
reported occurrence of TFA in precipitation, the lack of recent and comprehensive data
has severely limited the understanding of the significance of wet deposition as a source of
TFA to the (aquatic) environment. Thus, in the present work, a nationwide field monitoring
campaign covering all precipitation events over a one-year sampling period was
conducted at eight sites across Germany. Samples were analyzed for TFA using ion
exchange chromatography (IC) coupled to negative-ion electrospray tandem mass
spectrometry (ESI-MS/MS). Of the analyzed samples, 16% exhibited TFA concentrations
≥ 1 μg/L. The precipitation-weighted average TFA concentration of 0.34 μg/L highlighted
that wet deposition alone is responsible for approximately 0.3 to 0.4 μg/L of TFA in
surface waters in Germany. The annual wet deposition fluxes ranged from 91 to
400 μg/m², with the highest fluxes observed in densely populated regions. The annual wet
deposition of TFA for Germany during the observation period was estimated to be 68 t.
The sampling revealed a pronounced seasonality, with the highest concentrations and wet
deposition fluxes of TFA observed in summer. Pearson correlation analyses indicated that
the transformation of TFA precursors in the troposphere is enhanced in summer due to
elevated concentrations of photochemically generated oxidants, primarily •OH, which
ultimately results in increased atmospheric TFA deposition. Overall, the study provided the
first published data on TFA in precipitation in Germany since 1995/96. The derived data
serves as a benchmark for future studies. In addition, it allows for the establishment of
mass balances and can be used to develop models to predict the loads of TFA entering
the aquatic environment from multiple sources.
The lack of robust historical data on the wet deposition fluxes of TFA also impeded long-
term trend analyses. Specifically, a postulated increase in atmospheric formation and
deposition of TFA due to substantial emission increases of numerous volatile TFA
precursors in recent decades remained unquantified. To address this knowledge gap,
archived plant samples were analyzed to evaluate the long-term temporal trends in the
atmospheric deposition of TFA in Germany. A robust and highly sensitive analytical
method for TFA in plant matrices was developed and validated. The method
encompassed a three-step sequential extraction procedure followed by the analysis of the
diluted sample extracts using IC-ESI-MS/MS. Subsequently, archived leaf samples of
various tree species and sampling sites from the German Environmental Specimen Bank
(observation period: 1989−2020) were analyzed for TFA. Statistical analysis revealed
significant (p < 0.05) positive trends in TFA concentrations in plant leaves, which is likely
the result of both phytoaccumulation and increasing emissions of gaseous TFA precursors
over the observation period. The concentrations increased by factors of up to 12 from
1989 to 2020. The highest concentrations (up to ∼1,000 μg/kg dry weight) were found in
Lombardy poplar leaves. Overall, the study presents the first trend analysis of TFA in biota
and raises awareness of the escalating atmospheric deposition of TFA over the past three
decades.
Sulfamate has previously been identified as a TP of the artificial sweeteners cyclamate
and acesulfame in wastewater and drinking water treatment. The preliminary results
indicated that sulfamate concentrations in wastewater treatment plant (WWTP) effluent
are substantially higher than those of other wastewater-borne contaminants. However,
despite its high global production and usage, no information was available on the sources,
occurrence, and environmental significance of sulfamate in the aquatic system in
Germany. To close this knowledge gap, a quantitative monitoring approach of different
urban water cycle compartments was conducted. Target analysis based on IC-ESI-MS/MS
revealed exceptionally high concentrations of sulfamate in wastewater (up to 1,900 μg/L),
surface water (up to 580 μg/L), and finished drinking water (up to 140 μg/L) in Germany.
Considering the limited data on short-term ecotoxicity, approximately 30% of the
sulfamate concentrations detected in groundwater and surface water samples exceeded
the derived predicted no-effect concentration (PNEC) of sulfamate. Therefore, the
potential impact of sulfamate on the aquatic ecosystem in Germany cannot be excluded.
Municipal WWTP effluent was identified as the primary source of sulfamate for the aquatic
system, as its concentrations correlated positively (r > 0.77) with the municipal wastewater
tracer carbamazepine in samples from different waterbodies. Ozonation and activated
sludge experiments demonstrated that sulfamate can be formed through chemical and
biological degradation of various precursors containing a sulfonamide group.
Nevertheless, the transformation of precursors to sulfamate in WWTPs and receiving
waters was found to be quantitatively insignificant, due to the substantial direct use of
sulfamic acid as a descaling agent in domestic and industrial applications. Laboratory
batch experiments, in conjunction with the findings from the sampling conducted at full-
scale waterworks, demonstrated that the commonly applied drinking water treatment
techniques, including ozonation and activated carbon filtration, are largely ineffective in
removing sulfamate. Bank filtration was identified as the only option to efficiently eliminate
sulfamate from contaminated raw water resources (removal: 62% to 99%). Overall, the
study presents the first comprehensive analysis of sulfamate in the urban water cycle and
suggests that there may be other high production volume inorganic chemicals that are
currently overlooked in environmental studies and monitoring programs.
Despite pantoprazole (PPZ) being one of the most widely prescribed human
pharmaceuticals globally, consistently low concentrations of this proton-pump inhibitor in
environmental water samples have been documented. This can be attributed to the
extensive metabolism of PPZ within the human body, with only minor amounts of the
parent compound being excreted. Since environmental monitoring and risk assessment
for regulatory purposes focus on the parent substances of pharmaceuticals, it was
assumed that the current environmental exposure associated with the use of PPZ is
considerably underestimated. In the presented thesis, 4′-O-demethyl-PPZ sulfide (M1)
was identified as the most relevant PPZ metabolite for environmental analysis. This was
achieved by applying reversed-phase high-performance liquid chromatography (RP-
HPLC) coupled to high-resolution mass spectrometry (HRMS) to urine samples of a PPZ
user, as well as to municipal wastewater. M1, which had not been investigated in previous
monitoring studies, was found to be ubiquitous in WWTP influent and effluent (max.:
3 μg/L, detention frequency: 100%) as well as in surface water (max.: 1.2 μg/L; detection
frequency: 97%) in Germany. Its average surface water concentration was approximately
30 times higher than that of the parent compound PPZ. Moreover, quantitative structure-
toxicity relationship (QSTR) modeling indicated a lower preliminary freshwater PNEC for
M1 (4.8 μg/L) compared to PPZ (28 μg/L). The analysis of archived suspended particulate
matter (SPM) samples from the Rhine at Koblenz revealed that the concentrations of M1
increased significantly from 2005 to 2015 and were positively correlated with the
prescription volume of PPZ. Conventional biological wastewater treatment was found to
be insufficient to remove M1 (average removal: 22%). Laboratory-scale experiments and
the analysis of samples taken after different treatment steps of an advanced full-scale
WWTP demonstrated that post-treatment with activated carbon as well as ozonation can
significantly improve the removal of M1 and PPZ during wastewater treatment, thereby
reducing their release to the aquatic environment. During ozonation, a rapid oxidation of
M1 was observed, accompanied by the formation of several ozonation products, which
were proposed for the first time. The identity of the main ozonation TPs of M1 was
confirmed through the synthesis of reference compounds. Their detection in samples
collected after the ozonation step of a full-scale WWTP demonstrated the transferability of
the laboratory-scale ozonation experiments. M1 was found to be sufficiently removed from
contaminated source waters (max. raw water concentration: 0.25 μg/L) by bank filtration
under different redox conditions (removal ≥ 80 %) and by other commonly applied
purification processes in drinking water production. In summary, this study revealed that
the environmental exposure and risk associated with the use of PPZ have been previously
underestimated, which likely extends to other human pharmaceuticals. Therefore, these
findings call for more sophisticated approaches to environmental monitoring and risk
assessment of pharmaceuticals that take TPs into account.
This thesis provides an in-depth understanding of the entry paths, occurrence, fate, and
environmental significance of selected TPs in the aquatic system in Germany. It
significantly advances our understanding of the introduction of TFA into the water cycle,
by characterizing the source of wet deposition and elucidating long-term temporal trends
of atmospherically deposited TFA. Additionally, the thesis gives comprehensive insights
into the formation, behavior, removability, and potential (eco)toxicological risks of
sulfamate, PPZ and its TPs. The thesis addresses key challenges in assessing and
integrating TPs into chemical management and presents solutions to overcome these
challenges. Finally, it highlights the urgent need for increased focus on TPs in research,
aquatic monitoring, and regulation to safeguard the environment and human health.