M.Sc. / Two yellowfish species, namely Labeobarbus aeneus and Labeobarbus kimberlyensis were collected in the Vaal Dam and Vaal River Barrage over two years. The macroscopic characteristics, such as dimension and weight were recorded prior to dissecting out the gills. The gills were examined using a stereomicroscope for Paradiplozoon sp., the number of parasites was recorded and they were flat-fixed and stored in 10% Neutral Buffered Formalin. Statistical analysis of host yellowfish dimension and weight, and Paradiplozoon sp. occurrence was performed using Statistical Processing Software Suite v.15.00. The seasonal variation in size and shape of adult life-stage Paradiplozoon sp. attachment clamp sclerites was investigated using the geometric morphometric software Morphologika2 v. 2.5. Water quality variables at the Vaal Dam and Vaal River Barrage were analyzed using RAU Water v.2 software to produce a final Aquatic Toxicity Index Solway aggregate score. Diporpa, juvenile and adult stages of Paradiplozoon sp. were collected from yellowfish in the Vaal Dam, and oncomiracidia were allowed to hatch from eggs that were maintained in vitro. Details of life-stages were examined and measured using light microscopy, epi-fluorescence microscopy, confocal laser scanning microscopy, and scanning electron microscopy. The Solway aggregate score indicated that the water quality score in the Vaal Dam was better than the Vaal River Barrage. The water quality score was the poorest at both sites in the summer and best during the winter. Turbidity was identified to be the poorest water quality variable. No Paradiplozoon specimens were recovered from the gills of fish from 2005 to 2007 in the Vaal River Barrage. The numbers of Paradiplozoon sp. on yellowfish in the Vaal Dam were the greatest in winter at 67% prevalence, when the water quality score was the best during the study. In contrast to the elevated diplozoid numbers in rivers of poorer water quality in Europe, a low number of Paradiplozoon sp. were collected in spring when the water quality was poorer. This may be attributed to the difference in the type of aquatic pollutant in the Vaal River and European rivers. Yellowfish were longest and heaviest during spring, followed by autumn, summer and winter. It was not possible to statistically prove whether the presence of Paradiplozoon sp. negatively influences the size and weight of yellowfish. The increase in weight is suggested to be as a result of increased fat reserves, prior to spawning in spring.

Fishes are widely used by biologist as ecological indicators that measure key elements of complex systems, without having to capture the full complexity of a specific system. The Vaal River in South Africa is classified as Africa’s hardest working river and is home to, two yellowfish species that are socially and economically important. Both these yellowfish species are considered to be sensitive to changes in water quantity and quality, habitat destruction and utilisation pressure and are often used as ecological indicators to manage aquatic ecosystems. Very little however, is known about their movement, response to changing environmental variables and interspecies habitat preferences. This study therefore aims to use radio telemetry as a method to characterise and evaluate how yellowfish behaviour is influenced by changing environmental variables. To characterise the behavioural ecology of the Vaal-Orange River yellowfish species in lentic and lotic ecosystems, Labeobarbus aeneus (n=18) and L. kimberleyensis (n=3) were fitted with externally attached radio transmitters in Boskop Dam (L. aeneus, n=4) and the Vaal River (L. aeneus, n=14) (L. kimberleyensis, n=3). Various methods were used to collect yellowfish species including: gill nets, to target mobile individuals, in deep habitats, electro-fishing (electro-narcosis) to collect yellowfish in shallow habitats and angling techniques in a wide variety of habitats. Thereafter yellowfish species were sedated and tagged with externally attached radio transmitters, before being released back into the system. Yellowfish were monitored for eleven months using a remote monitoring system together with manual monitoring surveys. Analyses of data collected showed that L. aeneus follows distinct behavioural patterns, with some individual variations in behaviour. Labeobarbus aeneus exhibited higher movement that are associated with deeper water during daylight hours (04:00-16:00). During nocturnal periods (20:00-04:00) L. aeneus showed a decrease in movement activity and preferred shallower water compared to daytime. However, L. aeneus in the Vaal River seems to be less influenced by bright daylight and this might be due to the turbidity of the river water. Labeobarbus aeneus in Boskop Dam showed higher movement counts during full moon phases whereas L. aeneus in the Vaal River showed higher movement counts during new moon phases. All tagged fishes in Boskop Dam and in the Vaal River preferred deeper water during full moon phases than during new moon phases. Movement were significantly higher (P<0.05) with increased temperatures and shallower water in summer whereas movement significantly decreased (P<0.05) with a decrease in temperature and increased depth in autumn and winter. Seasonal movement data were, however, limited. This study confirms that radio telemetry methods can be used to characterise the behavioural ecology of yellowfish species. In addition, the study has improved the knowledge of how environmental variables may affect the behaviour of yellowfish species. However, due to limited data and our understanding of these species, it is still uncertain how behaviour of yellowfish species can be applied as an ecological indicator of aquatic ecosystems. / Thesis (MSc (Zoology))--North-West University, Potchefstroom Campus, 2013

Fishes are widely used by biologist as ecological indicators that measure key elements of complex systems, without having to capture the full complexity of a specific system. The Vaal River in South Africa is classified as Africa’s hardest working river and is home to, two yellowfish species that are socially and economically important. Both these yellowfish species are considered to be sensitive to changes in water quantity and quality, habitat destruction and utilisation pressure and are often used as ecological indicators to manage aquatic ecosystems. Very little however, is known about their movement, response to changing environmental variables and interspecies habitat preferences. This study therefore aims to use radio telemetry as a method to characterise and evaluate how yellowfish behaviour is influenced by changing environmental variables. To characterise the behavioural ecology of the Vaal-Orange River yellowfish species in lentic and lotic ecosystems, Labeobarbus aeneus (n=18) and L. kimberleyensis (n=3) were fitted with externally attached radio transmitters in Boskop Dam (L. aeneus, n=4) and the Vaal River (L. aeneus, n=14) (L. kimberleyensis, n=3). Various methods were used to collect yellowfish species including: gill nets, to target mobile individuals, in deep habitats, electro-fishing (electro-narcosis) to collect yellowfish in shallow habitats and angling techniques in a wide variety of habitats. Thereafter yellowfish species were sedated and tagged with externally attached radio transmitters, before being released back into the system. Yellowfish were monitored for eleven months using a remote monitoring system together with manual monitoring surveys. Analyses of data collected showed that L. aeneus follows distinct behavioural patterns, with some individual variations in behaviour. Labeobarbus aeneus exhibited higher movement that are associated with deeper water during daylight hours (04:00-16:00). During nocturnal periods (20:00-04:00) L. aeneus showed a decrease in movement activity and preferred shallower water compared to daytime. However, L. aeneus in the Vaal River seems to be less influenced by bright daylight and this might be due to the turbidity of the river water. Labeobarbus aeneus in Boskop Dam showed higher movement counts during full moon phases whereas L. aeneus in the Vaal River showed higher movement counts during new moon phases. All tagged fishes in Boskop Dam and in the Vaal River preferred deeper water during full moon phases than during new moon phases. Movement were significantly higher (P<0.05) with increased temperatures and shallower water in summer whereas movement significantly decreased (P<0.05) with a decrease in temperature and increased depth in autumn and winter. Seasonal movement data were, however, limited. This study confirms that radio telemetry methods can be used to characterise the behavioural ecology of yellowfish species. In addition, the study has improved the knowledge of how environmental variables may affect the behaviour of yellowfish species. However, due to limited data and our understanding of these species, it is still uncertain how behaviour of yellowfish species can be applied as an ecological indicator of aquatic ecosystems. / Thesis (MSc (Zoology))--North-West University, Potchefstroom Campus, 2013