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Generally speaking, protein import into mitochondria and chloroplasts is a post-translational process during which the precursor proteins destined for mitochondria or chloroplasts are translated with cytosolic ribosomes and targeted. The previous results showed that the isolated chloroplasts can import in vitro synthesized proteins and the absence of ribosomes in the immediate area around chloroplasts in electron microscopy (EM) images. However, none of the EM images were recorded in the presence of a translation elongation inhibitor. Also, the observation showed that ribosomes stably bind to purified liver mitochondria in vitro, and the first indication of chloroplast localization of mRNAs encoding plastid proteins in Chlamydomonas rheinhardtii, which challenge the post-translational import and support the co-translational process. Therefore, in this study, the association of the ribosomes to the isolated chloroplasts were analyzed, a binding assay was established and showed that naked ribosomes are not considerably bound to chloroplasts. Additionally, mRNA localize in close vicinity to mitochondria also challenged post-translation protein import. Global analysis of transcripts bound to mitochondria in yeast or human revealed that around half of the transcripts of mitochondrial proteins displayed a high mitochondrial localization. The observed association of mRNAs with chloroplast fractions and the in vivo analysis of the distribution of mRNAs was used as base to formulate the hypothesis that mRNA can bind to chloroplast surface. Therefore, in this study, the mRNA binding assay was established and revealed that mRNAs coding for the mitochondrial cytochrome c oxidase copper chaperone COX17 showed unspecific binding to the chloroplasts. The mRNA coding for chloroplast outer envelope transport protein OEP24 and mRNA coding for the essential nuclear protein 1 (ENP1) showed specific binding, and OEP24 has a 3-fold higher affinity than ENP1 mRNA. Moreover, the BY2-L (Nicotiana tabacum non-green cell culture) could confer the highest enhancement of OEP24 mRNA binding efficiency than the COX17 and ENP1 mRNA and the preparation of the BY2-L was optimized. Afterwards, the feasibility to fix the interaction between mRNA and the proteins on the surface of chloroplasts was confirmed. OEP24 mRNA showed more efficiency in the UV-crosslinking. Following, the pull-down with antisense locked nucleic acid (LNA)/DNA oligonucleotides was established which could be used for the further investigation of the proteins involved in the mRNA binding to the chloroplasts.
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.