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Institute
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.
A large number of chemicals are constantly introduced to surface water from anthropogenic and natural sources. Although substantial efforts have been made to identify these chemicals (e.g potentially anthropogenic contaminants) in surface waters using liquid chromatography coupled to high resolution mass spectrometry (LC-HRMS), a large number of LC-HRMS chemical signals often with high peak intensity are left unidentified. In addition to synthetic chemicals and transformation products, these signals may also represent plant secondary metabolites (PSMs) released from vegetation through various pathways such as leaching, surface run-off and rain sewers or input of litter from vegetation. While this may be considered as a confounding factor in screening of water contaminants, it could also contribute to the cumulative toxic risk of water contamination. However, it is hardly known to what extent these metabolites contribute to the chemical mixture of surface waters. Thus, reducing the number of unknowns in water samples by identifying also PSMs in significant concentrations in surface waters will help to improve monitoring and assessment of water quality potentially impacted by complex mixtures of natural and synthetic compounds. Therefore, the main focus of the present study was to identify the occurrence of PSMs in river waters and explore the link between the presence of vegetation along rivers and detection of their corresponding PSMs in river
water.
In order to achieve the goals of the present thesis, two chemical screening approaches, namely, non-target and target screening using LC-HRMS were implemented. (1) Non-target analysis involving a novel approach has been applied to associate unknown peaks of high intensity in LC-HRMS to PSMs from surrounding vegetation by focusing on peaks overlapping between river water and aqueous plant extracts (Annex A1). (2) LC–HRMS target screening in river waters were performed for about 160 PSMs, which were selected from a large phytotoxin database (Annex A2 and A3) considering their expected abundance in the vegetation, their potential mobility, persistence and toxicity in the water cycle and commercial availability of standards.
In non-target screening (Annex A1), a high number of overlapping peaks has been found in between aqueous plant extracts and water from adjacent location, suggesting a significant impact of vegetation on chemical mixtures detectable in river waters. The chemical structures were assigned for 12 pairs of peaks while several pairs of peaks
whose MS/MS spectra matched but no structure suggestion were made by the implemented software tools for retrieving possible chemical structure. Nevertheless, the pairs of peaks with matching spectra represented the same chemical structure. The identified compound belonged to different compound classes such as coumarins, flavonoids besides others. For the identified PSMs individual concentration up to 5 µg/L were measured. The concentration and the number of detected PSMs per sample were correlated with the rain event and vegetation coverage.
Target screening unraveled the occurrence of 33 out of 160 target compounds in river waters (Annex A2 and A3). The identified compounds belonged to different classes such as alkaloids, coumarins, flavonoids, and other compounds. Individual compound concentrations were up to several thousand ng/L with the toxic alkaloids narciclasine and
lycorine recording highest maximum concentrations. The neurotoxic alkaloid coniine from poison hemlock was detected at concentrations up to 0.4 µg/L while simple coumarins
esculetin and fraxidin occurred at concentrations above 1 µg/L. The occurrence of some PSMs in river water were correlated to the specific vegetation growing along the rivers while the others were linked to a wide range of vegetation. As an example, narciclasine and lycorine was emitted by the dominant plant species from Amaryllidaceae family (e.g. Galanthus nivalis (snow drop), Leucojum vernum and Anemone nemorosa) while intermedine and echimidine were from Symphytum officinale. The ubiquitous occurrence of simple coumarins fraxidin, scopoletin and aesculetin could be linked to their presence in a wide range of vegetation.
Due to lack of aquatic toxicity data for the identified PSMs (in both target and non-target) and extremely scarce exposure data, no reliable risk assessment was possible.
Alternatively, risk estimation was performed using the threshold for toxicological concern (TTC) concept developed for drinking water contaminants. Many of the identified PSMs
exceeded the TTC value (0.1 µg/L) thus caution should be taken when using such surface waters for drinking water abstraction or recreational use.
This thesis provides an overview of the occurrence of PSMs in river water impacted by the massive presence of vegetation. Concentration for many of the identified PSMs are well within the range of those of synthetic environmental contaminants. Thus, this study adds to a series of recent results suggesting that possibly toxic PSMs occur in relevant concentrations in European surface waters and should be considered in monitoring and risk assessment of water resources. Aquatic toxicity data for PSMs are extensively lacking but are required to include these compounds in the assessment of risks to aquatic organisms and for eliminating risks to human health during drinking water production.
Chemical pollution is one of the main contributors to the degradation of lotic ecosystems and their biodiversity. Among chemicals driving lotic biodiversity decline are anthropogenic organic micropollutants (AOM), which affect the survival and functioning of freshwater organisms. Continuous exposure of freshwater organisms to AOM leads to adverse effects that sometimes cannot be traced with standard toxicity methods such as standard toxicity testing or biodiversity indices. Among these effects of AOM are selective or mutagenic effects that cause impaired species genetic diversity. Thus, the correlation between different levels of AOM and genetic diversity of species is still poorly understood. However, it can be explored by applying population genetics screening.
In Chapter 1 of this thesis, background information on environmental pollution, genetic screening, and the detection of evolutionary-relevant AOM effects in freshwater organisms are described and the thesis goals are identified. The main goal of the thesis is to study whether AOM exposure occurring in European rivers causes a significant evolutionary footprint in freshwater species and leads to a selection of more tolerant geno-and phenotypes. Therefore, population genetics indices together with high-resolution chemical exposure screening of a widespread indicator invertebrate species, Gammarus pulex (Linnaeus, 1758), living in polluted and pristine European rivers were investigated.
In Chapter 2, the development of a genetic screening method for G. pulex (microsatellites) is described. Due to genetic differentiation and the presence of morphologically cryptic lineages, the available sets of target loci do not enable a reliable population genetic characterization of G. pulex from central Germany. Thus, a novel set of microsatellite loci for a high-precision assessment of population genetic diversity was here applied. Eleven loci were first identified and thereafter amplified in G. pulex from three rivers. The new loci reliably amplified and indicated polymorphisms in the studied amphipods. The amplification resulted in the successful identification of genetically distinct populations of G. pulex from the analyzed rivers. Moreover, the microsatellite loci were amplified in other genetic lineages of G. pulex and another Gammarus species, G. fossarum, promising a broader applicability of the loci in related amphipod species.
In Chapter 3, the effects of AOM on species genetic differentiation and sensitivity to toxic chemicals in a typical central European river with pristine and AOM-polluted sections was investigated. The river’s site-specific concentrations of AOM were assessed by chemical analysis of G. pulex tissue and water samples. To test, whether different levels of AOM in the river select for pollution-dependent genotypes, the genetic structure of G. pulex from the river was analyzed. Finally, the toxicokinetics of and sensitivity to the commonly used insecticide imidacloprid were determined for amphipods sampled at pristine and polluted sections to assess whether various levels of AOM in the river influence sensitivity of G. pulex to imidacloprid. The results indicated that different levels of AOM did not drive genetic divergence of G. pulex within the river but led to an increased sensitivity of exposed amphipods to imidacloprid. The amphipods living in polluted river sections were more sensitive to the insecticide due to chronic exposure to toxic levels of AOM.
In Chapter 4, the relationship between site-specific pollution levels of AOM and genetic diversity parameters of G. pulex was analyzed at the regional scale within six rivers in central Germany. The genetic structure of G. pulex in the studied area was tested for relatedness to the waterway distance between sites. Gammarus pulex genetic diversity parameters, including allelic richness and inbreeding rate, were tested against environmental pollution parameters using linear mixed-effect- and structural-equation models. According to the results, G. pulex genetic diversity parameters were significantly associated with the detected AOM levels. At sites with high concentrations of AOM and toxicity potential G. pulex showed reduced genetic diversity and increased rates of inbreeding. These results suggest that AOM play a major role in shaping the genetic diversity of G. pulex in rivers.
According to the findings presented here, the applied microsatellites can be used to successfully detect changes in genetic patterns in freshwater amphipods facing increased levels of AOM. The findings indicate that levels of AOM representative for European rivers do not lead to the separation of genotypes among G. pulex as the connectivity between sites majorly contributes to species’ genetic structure. However, the chronic exposure to increased levels of toxic AOM leads to a reduction of species genetic diversity and increases the sensitivity of G. pulex to the toxic chemical effects.