published_or_final_version / Environmental Management / Master / Master of Science in Environmental Management

published_or_final_version / Urban Planning / Master / Master of Science in Urban Planning

published_or_final_version / Environmental Management / Master / Master of Science in Environmental Management

Enteroviruses affect a broad segment of the population throughout the world and have been suspected to play a major role in waterborne disease for quite some time. The presence of these viruses in drinking water supplies constitutes a major health risk to the population because of their low infectious dose. The monitoring and study of these viruses in the environment have been limited by the current standard detection methodologies. Nucleic acid probe hybridization is a new and effective approach for the study and detection of these viruses in the environment. An important step in the detection of viruses in concentrated water samples by nucleic acid probes is the isolation of the viral genome from the water sample for hybridization. Previously, a series of time consuming organic extract ions was used to isolate viral RNA. This study reports the development of an alternative method for the isolation and preservation of viral RNA in environmental samples. Briefly, the sample is heated in the presence of an RNase inhibitor, and then applied to a hybridization membrane. This procedure has greatly reduced the time and difficulty of the assay while maintaining sensitivity and increasing consistency. This study reports the development and modification of a nonradioactive labeling system for the detection of viruses in water. Nonradioactive labels such as biotin offer several advantages over radioactive labels including unlimited shelf life, reduced cost and time of assay, and elimination of the radiation hazard. However, radioactive labels are generally the more sensitive method of detection. By combining direct and indirect labeling strategies, the sensitivity of this nonradioactive assay has been increased ten-fold. This assay can detect as little as 100 plaque forming units of poliovirus, only one order of magnitude less sensitive than radiolabeled probes. This assay is also ten-fold less sensitive than radiolabeled probes for the detection of enteroviruses in water samples. Nonradioactive probes offer a safe, inexpensive alternative to radiolabeled probes and tissue culture for the detection of viruses in the environment when ultrasensitivity is not required.

Rotaviruses are one of the most significant causes of diarrheal disease in the world. Their presence in groundwater and drinking water supplies constitutes a health risk to the population. The study of rotaviruses in the environment has been hampered by the lack of accessible and consistent detection methodologies. Gene probes and other molecular techniques are a novel approach for the detection of these viruses in water. The feasibility of these new techniques for the detection and study of rotaviruses in the environment has been assessed using the simian SA-11 and the culturable human Wa rotavirus strains as models. Two general approaches have been undertaken consisting of hybridization of probes with genomic RNA and hybridization with mRNA produced by the virion-incorporated transcriptase. Hybridization of gene probes with genomic dsRNA of rotaviruses in environmental concentrates resulted in the detection of 10 4 immunofoci of Wa rotavirus. In vitro transcription serves as an amplification method with sensitivity 100- to 1000-fold greater than when probing for genomic RNA. The sensitivity obtained in Wa-seeded distilled water and environmental concentrates after in vitro transcription is 2 and 20 immunofoci, respectively. Proteins in environmental concentrates decrease the efficiency of probe hybridization by 10-100 fold. Also, transcriptase-inhibiting factors found in environmental samples decrease the production of mRNA. Both proteins and transcriptase-inhibiting factors can be reduced significantly with Sephadex G-200 columns. Passage of environmental concentrate through Sephadex G-200 spun columns, followed by in vitro transcription, was used to detect rotaviruses in environmental samples. Rotaviruses were detected by this combination of techniques in eight of 20 sewage samples, one of 16 tap water samples, five of 32 ground water samples, and two of nine surface water samples. Only one of 17 samples which tested positive with Wa cDNA 4 was positive for non-specific probe binding. The probing of rotavirus mRNA, amplified by the virion-incorporated transcriptase, is a practical and feasible method for monitoring these viruses in the environment.

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The Lesotho Highlands Development Authority routinely uses the South African Scoring System version 4 (SASS4) in conjunction with water chemistry to monitor water quality of rivers in the Lesotho Highlands Water Project areas. The objective of this study was to test the efficiency of SASS4 in these areas.

As cyanobacteria (also known as blue green algae) produce a range of cyclic peptides which are highly toxic, capillary electrophoresis and associated techniques have been investigated to assess their applicability for toxin monitoring in the water bodies of kwaZulu Natal, South Africa. Capillary electrophoresis (CE) is a technique in which charged molecules can be efficiently separated in a buffer solution within a capillary tube under the influence of a strong electric field. Two CE modes, namely capillary zone electrophoresis (CZE) and micellar electrokinetic capillary chromatography (MECC) were initially evaluated using a laboratory-built CE instrument. The former mode lacked selectivity due to the similar charge to size ratio of the algal toxins. However, with the latter mode, incorporation of a surfactant (sodium dodecyl sulphate) into the buffer, produced sufficient resolution between components. Parameters including surfactant concentration, buffer ionic strength, buffer pH and operating voltage were systematically optimized to separate the four algal toxins under investigation (microcystin YR, microcystin LR, microcystin RR and nodularin). The optimum separation conditions were: 30 mM borax, 9 mM sodium dodecyl sulphate, pH 9.18, 30 kV applied voltage, 10 s hydrodynamic injection, 70 cm x 50 Ilm Ld. bare fused silica capillary (LEFF 40 cm) and UV detection at 238 nm. Under these conditions, typical detection limits were in the low ng/IlL range (14.13 ng/IlL for microcystin LR to 29.85 ng/ILL for nodularin). The MECC method was evaluated in terms of migration time precision, efficiency and resolution, peak area and normalised peak area precision. Standard deviation values for retention times acquired using replicate electrokinetic injections ranged from 0.018 to 0.054 and 0.069 to 0.148 for hydrodynamic injections. Normalised peak area precision for replicate hydrodynamic injections were in the range 84 to 97 % RSD, while improved % RSD values of 11.5 to 18.7 were achieved for electrokinetic injections. Due to poor precision resulting from the lack of automation on the laboratory built CE system, poor correlation between increasing concentration and a corresponding change in normalised peak areas were achieved. The MECC method developed was applied to the analysis of an algal scum extract to illustrate the technique. A general problem with CE is that it suffers from poor detection sensitivity. Hence in this study, alternative injection modes, sample concentration strategies and alternative detection techniques were investigated in an attempt to improve detection limits for algal toxins. Using optimized electrokinetic injection conditions, detection limits were five to ten times better than those obtained with hydrodynamic injections. On-line sample concentration methods were partially successful. Field amplified back and forth MECC in which analyte injected in the entire column volume and subsequently focused in a narrow band by manipulating the electric field, resulted in an enormous sensitivity enhancement that ranged from 197 times for microcystin RR to 777 times for microcystin YR when compared to hydrodynamic injections. Field amplified sample stacking (FASI) was ineffective for toxin preconcentration, while electro-extraction produced detection limits ranging from 0.27 ng/J.tL for microcystin YR to 1.08 ng/J.tL for microcystin RR. Solid phase extraction, in which analytes are first trapped and concentrated on HPLC material in a cartridge and then eluted in a more concentrated form for injection, was found to be practical only in the offline mode. A concentration detection limit of less than 0.002 ng/J.tL was obtained. Attempts with on-line solid phase extraction failed due to problems associated with coupling the cartridge with the separation capillary. Finally, laser induced fluorescence (LIF) detection was investigated as an alternative to UV detection. Unfortunately, the algal toxins were not amenable to LIF detection because tagging with the fluorescent moiety, fluorescein isothiocyanate (FITC), was prevented by the stereochemistry of these cyclic peptides. A comparative study between HPLC and MECC revealed that the former displayed poor efficiency peaks and long analysis times for toxin analysis. However HPLC was superior in terms of retention time precision (0.12 to 0.64 % RSD) and area precision (1.78 to 2.86 % RSD). Mass detection limits for MECC (0.0142 to 0.0603 ng) were far superior to those achieved by HPLC (0.55 to 1.025 ng). In addition to HPLC and MECC, a preliminary investigation of micro-high performance liquid chromatography (J.tHPLC) and capillary electrochromatography (CEC) for the analysis of algal toxins was made using 50 J.tm Ld. capillary columns packed in-house, with reverse phase HPLC packing material. / Thesis (M.Sc.)-University of Natal, 1997.