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Spinocerebellar ataxia type 2 (SCA2) is an autosomal dominant neurodegenerative movement disorder caused by expansion of CAG repeats in the ATXN2 gene beyond 33 units, while healthy individuals carry 22-23 repeats. First symptoms of SCA2 include uncoordinated movement, ataxic gait and slowing of the saccadic eye movements in line with the early pronounced atrophy of cerebellum, spinal cord and brainstem. Cerebellar Purkinje cells and spinal cord motor neurons are the most affected cells from ATXN2 expansions. Later on, patients manifest distal amyotrophy, problems in breathing and swallowing, depression and cognitive decline caused by widespread degeneration throughout the brain. The striking loss of mass in the brain, due to severe myelin fat atrophy, is accompanied by a similar reduction in the peripheral fat stores. After the devastating progression of disease, the severity and duration of which depends on the CAG repeat size, genetic background and environmental factors, patients succumb to SCA2 mostly because of respiratory failure at the terminal stage. Larger repeat sizes lead to an earlier manifestation of the disease and a more rapid progression. Aside from SCA2, intermediate-length and short pathogenic CAG expansions in ATXN2 between 26-39 repeats significantly increase the risk of developing other neurodegenerative disorders, such as amyotrophic lateral sclerosis (ALS), fronto-temporal lobar dementia (FTLD) or Parkinson plus tauopathies like progressive supranuclear palsy (PSP) in various cohorts across the world.
Ataxin-2 (ATXN2) is a ubiquitously expressed cytosolic protein most famous for its involvement in neurodegenerative disease caused by the expanded poly-glutamine (polyQ) domain corresponding to a genomic (CAG)n tract. This N-terminal polyQ domain has no known function, other than increasing the aggregation propensity of mutant ATXN2 and facilitating interaction with other polyQ containing proteins, leading to their sequestration. The progressive accumulation of ATXN2 into cytosolic foci, and also that of its interaction partners over time, underlies the molecular pathomechanism. Next to polyQ domain, ATXN2 also contains a Like-Sm domain (Lsm), an Lsm-associated domain (LsmAD), multiple proline-rich domains (PRD) and a Poly(A)-Binding-Protein (PABP)-interacting motif (PAM2).
Through its Lsm/LsmAD domains, ATXN2 directly binds to a large number of transcripts, regulating their quality and translation rate. In a similar fashion, through its direct interaction with PABP via PAM2 motif, ATXN2 indirectly modifies the fate of even larger number of transcripts and global translation. Several PRDs scattered across the protein help ATXN2 associate with growth factor receptors and other endocytosis factors, modulating nutrient uptake and downstream signaling.
ATXN2 is a stress response factor. Therefore, its involvement in nutrient uptake plays a crucial part in cell’s capability to overcome non-permissive conditions. Upon nutrient deprivation, oxidative stress, proteotoxicity, heat stress or Ca2+ imbalance, ATXN2 relocalizes into cytosolic ribonucleoprotein particles known as stress granules (SGs), together with PABP, several eukaryotic translation initiation factors, many other RNA-binding proteins (RBP) with their target transcripts and the small ribosomal subunit. Collectively, they modulate the stability of the trapped transcripts, favoring the maturation and translation of IRES-dependent stress response proteins instead, according to the specific need. Many RBPs interact either directly or in an RNA-dependent manner in the SGs, and due to the large number of ALS-causing mutations identified in them (such as TDP-43, FUS, TIA-1, hnRNPA2/B1), SGs became a hot topic in neuropathology. Acute SGs serve to halt translation and growth, and to spend energy only for survival until stress disappears. However, chronic SG assembly eventually activates apoptotis leading to cell death. While the polyQ expansions in ATXN2 enhance SG stability, reduce their dissociation rate after stress, and lead to aberrant post-translational modifications of other SG components like TDP-43, complete loss of ATXN2 delays SG formation and results in easily dissolvable foci.
Most of the stressors that induce SG formation eventually converge on energetic deficit. Therefore, it is logical that the ultimate task of SGs is to stop further growth when it cannot be afforded. In yeast, the molecular mechanism underlying this growth arrest was explained as sequestration of the master growth regulator complex, Target-of-Rapamycin Complex 1 (TORC1), into SGs in an ATXN2-dependent manner. The repressor effect of ATXN2 on mammalian TORC1 (mTORC1) and global protein translation had already been documented in earlier studies; complete loss of ATXN2 function in knock-out mouse (Atxn2-KO) resulted in mTORC1 hyperactivity and transcriptional upregulation of multiple ribosomal subunits indicating an increased need for these machines. ...
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.