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Capillary electrophoresis and related techniques for the analysis of fresh water algal toxins.

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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 Ld. capillary columns packed in-house, with reverse phase HPLC packing material.


Thesis (M.Sc.)-University of Natal, 1997.


Cyanobacteria., Algal toxins., Water--Pollution--Toxicology., Theses--Chemistry.