"January 2003" / Amendments in pocket inside back cover. / Bibliography: leaves 212-229. / xi, 229 leaves : ill. (some col.), map, plates (col.) ; 30 cm. / Title page, contents and abstract only. The complete thesis in print form is available from the University Library. / Thesis (Ph.D.)--University of Adelaide, School of Earth and Environmental Sciences, Discipline of Environmental Biology, 2003

Reservoirs are the main drinking water sources in Taiwan. However, about half of 23 reservoirs suffer the eutrophication problems based on the calculated Carlson¡¦s TSI indexes for them. Thus, the reservoir water is seriously polluted. Chen-Ching Lake Reservoir, Fengshan Reservoir, and A-Kong-Tien Reservoir are three major reservoirs that supply water for the domestic, industrial, and agricultural uses in the Kaohsiung area. Due to the long-term sediment deposition at A-Kong-Tien Reservoir, a sediment dredge system is under construction at this reservoir. Thus, only Chen-Ching Lake Reservoir and Fengshan Reservoir play the most important roles in water supply at this moment. However, both Chen-Ching Lake Reservoir and Fengshan Reservoir are in the list of the most eutrophized reservoirs. There are several ways to evaluate the status of eutrophication of reservoirs. The single-index method and multi-variable modeling method are two of the most commonly methods for water quality analysis and eutrophication evaluation for the reservoirs in Taiwan. Based on the analytical results from previous studies, eutrophication results in the fast growing of seaweeds and they spread and cover the whole water bodies, which is called algal bloom. The type of seaweed causing eutrophication in Taiwan reservoirs are mainly Cyanobacteria, especially the commonly found Microcystis. They can not only cause some foul smells but release toxins into the water bodies. That endangers the safety of drinking water and affects the normal water usage. To prevent eutrophication, the nutrients loadings outside and inside of the reservoir areas must be reduced and controlled, which can effectively prohibit the growth of seaweeds. An air-pumping system can also be built for the same purpose. Regular water quality inspection should be carried out to monitor the fluctuation of water quality.

Bibliography: leaves 252-267. / xvi, 267 leaves : ill. ; 30 cm. / Title page, contents and abstract only. The complete thesis in print form is available from the University Library. / These cyanobacteria are two freshwater phytoplankton which produce toxins, taint the taste and odour of potable water and form surface blooms. A technique was developed to assess cell metabolic activity and to determine the influence of light and nutrients on gas reside synthesis and bouyancy regulation in order to understand factors which favour their dominance, and thus how to control them. / Thesis (Ph.D.)--University of Adelaide, Dept. of Botany, 1998?

Thesis (Ph.D.)-University of California, Santa Cruz, 2007. / Includes bibliographical references. Also available online. Restricted to UC campuses.

Thesis (M.S.)--University of North Carolina at Wilmington, 2005. / Includes bibliographical references (leaves: [70]-74)

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.

This work investigates, for the first time, the Pseudo-nitzschia (PN) dynamics in the western English Channel (L4) and the environmental factors impacting on domoic acid (DA) production in these waters. This is combined with laboratory studies examining key environmental factors and the multifactorial impact of multiple macronutrient and micronutrient availability on PN growth and DA production. An LC-MS method was established, optimised, and compared with ELISA for the accurate and reproducible extraction and determination of particulate and dissolved DA. The method was used to measure the seasonal variation in DA at L4 during 2009 and this was compared to PN seasonal abundance and diversity. Three groups a P. delicatissima-group, a P. seriata-group, and a P. pungens/multiseries-group were identified and were found to have different ecological distributions with the latter two groups significantly correlating with DA concentration. Macronutrients, in combination with other environmental factors, were found to influence PN populations at L4. Multifactorial laboratory culture experiments investigating the availability of nitrate, phosphate, and silicate, confirmed that the interrelatedness of all these nutrients significantly affected the growth, decline, and DA production of P. multiseries, and highlight the importance of both phosphate and silicate availability for DA production. When the impacts of both macronutrient (phosphate and silicate) and micronutrient (iron and copper) availability were investigated, limited growth and DA production was observed in P. multiseries cultures. Results revealed the complexity and interrelationship of factors affecting both PN growth and DA production. Furthermore, molecular methods were developed to elucidate the PN species present from 2009 Lugol’s-preserved L4 samples. DNA was successfully extracted and amplified from these samples which had been stored for up to 2 years. Initial sequence analysis identified the rbcL DNA marker as an informative site for future work with a number of L4 sequences closely relating to different Pseudo-nitzschia spp.

Thesis (M.S.)--University of North Carolina at Wilmington, 2006. / Includes bibliographical references (leaves: 36-40)

Thesis (M.S.)--University of North Carolina at Wilmington, 2005. / Includes bibliographical references (leaves: [52]-58)

The purposes of this study were to characterize the complexation of toxic metals with algal toxins and to determine the effects of arsenic and copper on the growth of Karenia brevis under specific experimental conditions. Microcystins, pahayokolides, brevetoxins and okadaic acid were used as representatives of algal toxins while arsenic, copper, cadmium, cobalt, iron, manganese and mercury were selected as typical toxic metals (including metalloids here) in the aquatic environment. The stabilities of the toxin-metal complexes were determined using equilibrium dialysis and/or centrifugal ultrafiltration technique. A direct exposure of arsenic and copper to the K. brevis was carried out to determine the effects of these metals to the growth of the algal cell. The results indicated that Cu2+, Hg2+, Co2+, Cd2+ and Fe2+ were capable of complexing with the algal toxins. Moreover, the exposure experiments demonstrated that the high concentration of arsenic and copper could affect the growth of the K. brevis.