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Water quality modulation of aluminum toxicity to rainbow trout (Oncorhynchus mykiss) : biological and physiological approachesGundersen, Deke T. 13 December 1994 (has links)
Graduation date: 1995
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The influence of aluminium on enzymes in the rat brain with special reference to those involved in polyanine biosynthesisLi, Ching-lu., 李淸露. January 1988 (has links)
published_or_final_version / Medical Sciences / Master / Master of Medical Sciences
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Influence of water hardness on gill accumulation and acute toxicity of aluminum in rainbow troutBustaman, Sjahrul 14 January 1992 (has links)
Rainbow trout were exposed to aluminum at pH 7.25 and
8.25 and four hardnesses (10, 30, 80, and 120 ppm CaCO₃)
for 96 hours in a continuous-flow system and mortality and
aluminum accumulation in the gills were determined.
Temperature, pH, and dissolved oxygen were measured
daily for each treatment. Dissolved and total aluminum
concentrations and hardness were determined following exposure
periods of 48 and 96 hours. Aluminum was most toxic
at pH 8.25, and was more toxic at lower than at higher
hardnesses. Water hardness provided a significant protective
effect against aluminum-induced mortality (p < 0.05),
and there were no significant effects for water hardness on
gill accumulation at either of pH. At pH 7.25 no mortalities
occurred under any conditions. At pH 8.25, the accumulation
of aluminum in gill tissues was higher than for pH
7.25 following exposure for 96 hours.
In addition, aluminum concentration and exposure time had a
significantly cumulative effect on fish mortality (p <
0.05).
Possible mechanisms for aluminum toxicity and the
accumulation of aluminum in the gills of rainbow trout were
attributed to the forms and solubilities of aluminum species
at different pH values. Competition between Ca²⁺ and
aluminum for binding sites on the gills likely influenced
aluminum toxic action. / Graduation date: 1992
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Bioaccumulation of metals in selected fish species and the effect of ph on aluminium toxicity in a cichlid oreochromis mossambicusCoetzee, Lizet 24 August 2012 (has links)
M.Sc. / The upper catchment of the Olifants River, from its origin near Bethal, to its confluence with the Wilge River, north of Witbank, as well as it tributaries, are being subjected to increasing afforestation, mining, power generation, irrigation, domestic and industrial activities. These activities have a profound effect on the water quality and the major point sources of pollution in this area include mines, industries and very importantly, combined sewage purification works, located alongside the river, which, in addition to oxidizable material contains detergents, nutrients, and metals. It was therefore necessary to determine the extent to which these activities affect the water quality of the system. The impact of these activities was therefore addressed by a Water Research Commision Project namely "Lethal and sublethal effects of metals on the physiology of fish" of which the present study investigated effects at two localities, namely in the Olifants River (locality OR1) before its confluence with the Klein Olifants River and a locality in the Klein Olifants River (locality KOR1). Apart from the field study, toxicity tests were also performed in a laboratory, in order to determine the effects of low pH and elevated aluminium concentrations on the haematology, osmoregulation and carbohydrate metabolism of the Mozambique Tilapia, Oreochromis mossambicus as the acidification of soil systems may cause the transfer of aluminium into aqueous solutions, where it may be present in different forms. During the field study, the chemical and physical characteristics of the river water were evaluated, with special attention to the concentrations of certain metals (manganese, copper, chromium, lead, nickel, zinc, iron and aluminium) in the water and sediment, as well as in fish, which are known to accumulate the elements supra and are therefore valuable as indicators of these pollutants. The two fish species used for the investigations were the African sharptooth catfish, Clarias gariepinus and the moggel, Labeo umbratus. Four tissue types were dissected, namely the muscle, liver, skin and gill tissues. The metal concentrations in these organs/tissues, as well as in the water and sediment, were determined in a laboratory with an atomic absorption spectrophotometer. Statistical analyses were performed on the results obtained from this study and the order and extent of bioaccumulation of these metals in the water and sediment were determined, as well as in the fish organs/tissues. Its dependence on the size, sex and species of the fish and the localities and seasons were investigated.
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The role of copper in the apparent aluminum toxicity of aquatic systemsO'Reilly, Kirk Thomas 01 January 1985 (has links)
The effect of variations in aluminum and copper concentrations on the growth rate and enzyme activity of the green alga Scenedesmus quadricauda was investigated. The goal was to determine which chemical species control the biological parameters. The computer program MINEQL (Westal et al 1976) was used to estimate chemical speciation. In the prevalence of both metals, algal growth rate and alkaline phosphatase activity could be correlated to cupric ion activity. The activity of isolated bacterial alkaline phosphatase was found to be a function of both total copper concentration and cupric ion activity. A model was developed to predicted the effects on alkaline phosphatase of perturbation in aquatic chemistry.
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Influence of heat, aluminium toxicity and exposure to Bacillus subtilis on the germination of Abelmoschus esculentusMathiba, Matsobane Taboga 25 February 2016 (has links)
Okra (Abelmuschus esculentus (L) Moench.) is one of the most popular crops within the Malvaceae family of plants. It is a common vegetable eminently cultivated in regions experiencing constraints to manage climate change. In South Africa climate change coupled with aluminium-enriched soils are responsible to drawbacks crop performance. Therefore, it is worthwhile to whether okra will thrive as an alternative crop in the country. Many studies have identified potential of okra to improve yields of resource poor farmers in Africa. The physiological responses of okra seed to variations in aluminium ions and temperature were not determined. Therefore, a study with okra, cv. Clemson Spineless, seed coated and uncoated with B. subtilis, was initiated to assess germination on moist filter paper in 90mm diameter Petri plates. Germination medium consisted of various concentrations of aluminium chloride (AlCl3), 0M, 0.001M, 0.01M, 0.05M and 0.1M. Each aluminium treatment was allocated into incubators adjusted to 22°C, 25°C and 37°C temperatures. This resulted into a 5 x 3 x 2 factorial experiment with five replicates and was conducted in three cycles. Daily scores of germinated seeds were assessed from the second to the fifth day after initiation of germination. During termination, five days after the initiation of the experiment 10 seeds with the longest coleoptiles had their coleoptiles measured using a digital caliper. At the fifth day after initiation of the experiment, coleoptile lengths from 10 seeds per treatment were measured using digital caliper. A total of 50 plates (10 from 37°C in Cycle 1; 30 from 22°C, 25°C and 37°C from Cycle 2; 10 from 37°C in Cycle 3), were selected and germinated were ground and stored at - 20°C before 1H NMR analysis. Metabolites were extracted from 50mg ground seed material with 750 μL methanol-D4 and 750 μL buffer (deuterium oxide + potassium dihydrogen phosphate). The mixture was vortexed for three minutes, sonicated for 20 minutes, centrifuged at 18000 rpms for 20 minutes and the supernatant filtered through cotton wool. Then the supernatant was dispensed into NMR tubes for further 1H NMR spectroscopic processing using a 600 MHz NMR xiii
Varian spectrometer to generate magnetic spectra of the fifty samples. Results of this study demonstrated that in all the experimental cycles, regardless of aluminium concentration and bacterial seed coating, 37°C inhibited germination percentages and coleoptile lengths in okra seed germination. Germination percentages and coleoptile lengths of bacteria-coated seeds growing in 25°C were most stimulated at all aluminium concentrations, but not at 0.1M. In this temperature germination percentages and coleoptile lengths were highly influenced by the interaction of aluminium concentrations and bacterial coating, respectively. 1H NMR metabolomic association showed no distinct grouping, but clusters across treatments showed to be linked through a subset of metabolites amongst aluminium concentrations, bacterial seed coating and temperatures, respectively. This infers that treatment variations in both seed and bacterial physiological responses were associated through shared metabolic pathways. In conclusion, the study proved that 25°C provide temperature environment within which B. subtilis can be able to stimulate growth and remediate physiological constraints from aluminium ions during okra seed germination. / Agriculture, Animal Health and Human Ecology / M. Sc. (Agriculture)
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Influence of heat, aluminium toxicity and exposure to Bacillus subtilis on the germination of Abelmoschus esculentusMathiba, Matsobane Taboga 25 February 2016 (has links)
Okra (Abelmuschus esculentus (L) Moench.) is one of the most popular crops within the Malvaceae family of plants. It is a common vegetable eminently cultivated in regions experiencing constraints to manage climate change. In South Africa climate change coupled with aluminium-enriched soils are responsible to drawbacks crop performance. Therefore, it is worthwhile to whether okra will thrive as an alternative crop in the country. Many studies have identified potential of okra to improve yields of resource poor farmers in Africa. The physiological responses of okra seed to variations in aluminium ions and temperature were not determined. Therefore, a study with okra, cv. Clemson Spineless, seed coated and uncoated with B. subtilis, was initiated to assess germination on moist filter paper in 90mm diameter Petri plates. Germination medium consisted of various concentrations of aluminium chloride (AlCl3), 0M, 0.001M, 0.01M, 0.05M and 0.1M. Each aluminium treatment was allocated into incubators adjusted to 22°C, 25°C and 37°C temperatures. This resulted into a 5 x 3 x 2 factorial experiment with five replicates and was conducted in three cycles. Daily scores of germinated seeds were assessed from the second to the fifth day after initiation of germination. During termination, five days after the initiation of the experiment 10 seeds with the longest coleoptiles had their coleoptiles measured using a digital caliper. At the fifth day after initiation of the experiment, coleoptile lengths from 10 seeds per treatment were measured using digital caliper. A total of 50 plates (10 from 37°C in Cycle 1; 30 from 22°C, 25°C and 37°C from Cycle 2; 10 from 37°C in Cycle 3), were selected and germinated were ground and stored at - 20°C before 1H NMR analysis. Metabolites were extracted from 50mg ground seed material with 750 μL methanol-D4 and 750 μL buffer (deuterium oxide + potassium dihydrogen phosphate). The mixture was vortexed for three minutes, sonicated for 20 minutes, centrifuged at 18000 rpms for 20 minutes and the supernatant filtered through cotton wool. Then the supernatant was dispensed into NMR tubes for further 1H NMR spectroscopic processing using a 600 MHz NMR xiii
Varian spectrometer to generate magnetic spectra of the fifty samples. Results of this study demonstrated that in all the experimental cycles, regardless of aluminium concentration and bacterial seed coating, 37°C inhibited germination percentages and coleoptile lengths in okra seed germination. Germination percentages and coleoptile lengths of bacteria-coated seeds growing in 25°C were most stimulated at all aluminium concentrations, but not at 0.1M. In this temperature germination percentages and coleoptile lengths were highly influenced by the interaction of aluminium concentrations and bacterial coating, respectively. 1H NMR metabolomic association showed no distinct grouping, but clusters across treatments showed to be linked through a subset of metabolites amongst aluminium concentrations, bacterial seed coating and temperatures, respectively. This infers that treatment variations in both seed and bacterial physiological responses were associated through shared metabolic pathways. In conclusion, the study proved that 25°C provide temperature environment within which B. subtilis can be able to stimulate growth and remediate physiological constraints from aluminium ions during okra seed germination. / Agriculture, Animal Health and Human Ecology / M. Sc. (Agriculture)
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