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Taxonomy, phylogeny and zoogeography of the hexaploid Torini of the Middle East and North Africa
(2017)
Fishes of the tribe Torini Karaman, 1971 (Teleostei: Cyprinidae) are a diverse group of primary freshwater fishes, distributed in Africa, the Middle East, and Indomalaya. They are an important component of the native freshwater-fish fauna of the Middle East and North Africa, and occur in most large river systems of the Levant, Arabia, Mesopotamia, southern Iran, and Morocco. They belong to the subfamily Cyprininae, are characterised by being tetraploid or hexaploid, having large scales, and a smooth and ossified last unbranched ray in the dorsal fin. As primary freshwater fishes they are not able to tolerate marine conditions and depend on direct freshwater connections for their dispersal. This makes them an ideal model for zoogeographic studies.
Prior to this study, the diversity of the Torini species in the Middle East and North Africa was not well understood. The validity of several genera and species was unclear, and the generic assignment of several species changed frequently.
In this PhD project the taxonomy, phylogeny, and zoogeography of the Torini of the Middle East and North Africa were investigated with morphological, as well as molecular methods. More than 1550 fish specimens were examined morphologically. Some of the specimens, including the types of most nominal species, were already available from museum collections. The remaining specimens were collected during expeditions to Ethiopia, Iran, Jordan, Morocco and Syria. Tissue samples were collected for molecular genetic analyses. The mitochondrial genes for cytochrome b, NADH dehydrogenase subunit 4 and the tRNAs for serine and histidine were sequenced from more than 120 specimens, representing 20 species of Torini and two small, diploid African barbs (Cyprinidae, tribe Smiliogastrini). Molecular data were analysed with Bayesian inference and other methods.
The analyses confirmed that the hexaploid Torini of Africa and the Middle East form a monophyletic group. In the Middle East and North Africa the Torini are represented by the genera Arabibarbus, Carasobarbus, Mesopotamichthys, and Pterocapoeta. These genera are each morphologically diagnosable, monophyletic, and genetically distinct. The species 'Labeobarbus' reinii cannot be assigned to any of these genera, because it is morphologically dissimilar and genetically clearly separated from each of them. A generic name for this species is presently not available and until the description of a new genus it is preliminarily assigned to the genus 'Labeobarbus'.
Out of the 28 species-group taxa described from the Middle East and North Africa until now, 15 are valid: Arabibarbus arabicus, A. grypus, A. hadhrami, Carasobarbus apoensis, C. canis, C. chantrei, C. exulatus, C. fritschii, C. harterti, C. kosswigi, C. luteus, C. sublimus, Mesopotamichthys sharpeyi, Pterocapoeta maroccana, and 'Labeobarbus' reinii.
The phylogenetic relationships between the Middle Eastern and North African Torini are well resolved, based on the analysis of mitochondrial DNA sequences from nearly all relevant species.
The interspecific and intraspecific morphological and genetic diversity is shaped by the zoogeographic history. Conclusions can be drawn about the events that shaped the evolution of this group. The Torini originated in the Indomalayan biogeographical realm and colonised the Middle East and Africa during the Miocene via the Gomphotherium landbridge. The Indomalayan Torini are tetraploid, whereas those of the Middle East and Africa are hexaploid. Molecular phylogenetic analyses showed that the hexaploid Torini cluster within the tetraploid Torini. This makes the tetraploid Torini a paraphyletic group with respect to the hexaploid Torini. Morocco was colonised in two independent waves. The first came from sub-Saharan Africa and is represented by Pterocapoeta maroccana. The second originated in the Middle East and gave rise to C. fritschii, C. harterti, and probably 'L.' reinii. The Tigris-Euphrates system is the largest freshwater system in the Middle East. Its central position between the Orontes River and Jordan River in the West, the Iranian tributaries to the Persian Gulf in the East, and the Arabian Peninsula in the South made it an important crossroad for the colonisation of the Middle East by Torini and other freshwater biota. During the Miocene the predecessors of the Jordan and Orontes rivers were connected to the Tigris-Euphrates system. The Jordan River was separated from the Euphrates before the Orontes. Arabia was colonised in two waves. The first (A. arabicus, A. hadhrami, C. exulatus) dates to the Pliocene, whereas the second (C. apoensis) ended as recently as the late Pleistocene or early Holocene.
Surface water can contain a complex mixture of organic micropollutants (i.e. residues of pharmaceuticals or biocides). Conventional wastewater treatment plants (WWTPs) do not completely remove a broad range of anthropogenic chemicals and therefore represent a leading point source. To upgrade WWTPs, technical solutions based on oxidative and sorptive processes have been developed and successfully implemented. Acknowledging these substantial advances, this thesis focuses on another key topic and aims to investigate whether improved biological treatment processes likewise effectively remove anthropogenic micropollutants from wastewater. The work conducted on this topic was part of two European research projects (ATHENE, ENDETECH).
The ATHENE project aimed to go beyond the state-of-the-art by developing biological wastewater treatment processes that exploit the full potential of biodegradation. With the objective to explore the potential of complementary strictly anaerobic conditions within the biological wastewater treatment, combinations of aerobic and anaerobic treatments on site of a WWTP were implemented. Based on pre-experiments, two promising treatment combinations were selected for a more comprehensive evaluation. An aerobic treatment was paired with an anaerobic pre-treatment under iron-reducing conditions, and an activated sludge treatment was combined with an anaerobic post-treatment under substrate-limiting conditions. For the evaluation of these processes, an effect-based assessment was applied and combined with chemical data of 31 selected target organic micropollutants as well as ten metabolites. To assess the removal of endocrine disrupting chemicals (EDCs), yeast based reporter gene assays covering seven receptor-mediated mechanisms of action including (anti-)estrogenicity, (anti-) androgenicity, retinoid-like, and dioxin-like activity were conducted. Furthermore, the removal of unspecific toxicity (Microtox assay) and oxidative stress response as a marker for reactive toxicity (AREc32 assay) were analyzed to cover micropollutants acting via a non-specific mechanism of action. Moreover, to assess toxicity of the whole effluent in vivo, standardized in vivo bioassays with four aquatic model species (Desmodesmus subspicatus, Daphnia magna, Lumbriculus variegatus, Potamopyrgus antipodarum) were performed.
The combination of aerobic and anaerobic treatments resulted in a low additional removal of the selected target organic micropollutants (by 14-17%). In contrast, the removal of endocrine and dioxin-like activities (by 17-75%) and non-specific in vitro toxicities (by 27-60%) was significantly enhanced. Compared to technical solutions (i.e. ozonation), the combination with an anaerobic pre-treatment under iron-reducing conditions was likewise effective in removing the estrogenic activity as well as the unspecific toxicity, whereas anti-androgenic activity and dioxin-like activity were less effectively removed. Exposure to effluents of the conventional activated sludge treatment did not induce adverse in vivo effects in the investigated aquatic model species. Accordingly, no further improvement in water quality could be observed. In conclusion, the combination of aerobic and anaerobic treatment processes significantly enhanced the removal of specific and non-specific in vitro toxicities. Thus, an optimization of the biological wastewater treatment can lead to a substantially improved detoxification. These capacities of a treatment technology can only be uncovered by complementary effect-based measurements.
The global objective of the ENDETECH project was to develop a biotechnological solution to eliminate recalcitrant pharmaceuticals in wastewater direct from sites, where high loads are expected (i.e. hospitals). For this purpose, laccase, an enzyme mainly found in wood decaying fungi, was immobilized on ceramic membranes for application in bioreactors. In a proof of principle experiment, the performance of immobilized laccase in removing a mixture of 38 antibiotics without and in combination with a natural mediator (syringaldehyde; SYR) was investigated. For the evaluation of the enzymatic membrane bioreactors, chemical data on the elimination of the selected target antibiotics was combined with the outcomes of two in vitro bioassays. Growth inhibition tests with an antibiotic sensitive Bacillus subtilis strain were conducted to assess the residual antibiotic activity of the effluents, and Microtox assays were performed to detect a potential formation of toxic by-products.
The treatment by laccase without SYR did not reduce the load of antibiotics significantly. In contrast, in combination with a SYR concentration of 10 µmol L-1, 26 out of 38 antibiotics were removed by >50% after 24 h treatment. Moreover, increasing the SYR concentration to 1000 µmol L-1 resulted in a further improvement of the antibiotic removal. 32 out of 38 antibiotics were removed by over 50%, whereby 17 were almost completely eliminated (>90%). However, the treatment with laccase in combination with SYR resulted in a time-dependent increase of unspecific toxicity. While SYR alone did not affect B. subtilis, the combination of laccase with SYR led to a strong time-dependent growth inhibition up to 100%. Similar to that, a time-dependent increase of unspecific toxicity in the Microtox assay was observed. In conclusion, the laccase-mediator process successfully degrades a broad spectrum of antibiotics and thus represents a promising technology to treat wastewater from sites, where high loads are expected. However, further research is required to reduce the formation of unspecific toxicity before an implementation of this technology can be considered.