This book describes the present state of knowledge regarding the impact of cyanobacteria on health through the use of water. It considers aspects of risk management and details the information needed for protecting drinking water sources and recreational water bodies from the health hazards caused by cyanobacteria and their toxins. It also outlines the state of knowledge regarding the principal considerations in the design of programmes and studies for monitoring water resources and supplies and describes the approaches and procedures used.
The development of this publication was guided by the recommendations of several expert meetings concerning drinking water (Geneva, December 1995; Bad Elster, June
1996) and recreational water (Bad Elster, June 1996; St Helier, May 1997). An expert meeting in Bad Elster, April 1997, critically reviewed the literature concerning the toxicity of cyanotoxins and developed the scope and content of this book. A draft manuscript was reviewed at an editorial meeting in November 1997, and a further draft was
reviewed by the working group responsible for updating the Guidelines for Drinkingwater Quality in March 1998.

/pdf/toxic-cyanobacteria-in-water-a-guide-to-their-public-health-2y64v55hv1.pdf

Toxic cyanobacteria in water: a guide to their public health consequences, monitoring and management.

(2002). The Effects of Harmful Algal Blooms on Aquatic Organisms. Reviews in Fisheries Science: Vol. 10, No. 2, pp. 113-390.

The Effects of Harmful Algal Blooms on Aquatic Organisms

A Unified Approach to Marine Plant-Herbivore Interactions. I. Populations and Communities

Examination of the results of routine assays for hepatic enzymes in plasma has shown a significant elevation of the levels of gamma-glutamyl-transpeptidase, and a lesser elevation of those of alanine aminotransferase, in plasma specimens from a population who obtained drinking water from a reservoir containing a heavy bloom of toxic Microcystis aeruginosa. Such elevations did not occur in the adjacent population who did not use water from this source. They coincided with the occurrence of the algal bloom, and were not present in the corresponding assays during the periods before and after the occurrence of the bloom. Increases in the levels of these enzymes indicate toxic liver injury and could not be attributed to clinical changes in the frequency of acute liver conditions or to variations in the number of plasma samples taken from patients with alcoholism. Therefore, it is concluded that the toxic algae in the water-supply reservoir cause the observed elevation of the levels of hepatic enzymes in the plasma of the consuming population.

Evidence of liver damage by toxin from a bloom of the blue-green alga, Microcystis aeruginosa.

Hepatotoxic microcystins (MCs) are the most widespread class of cyanotoxins and the one that has most often been implicated in cyanobacterial toxicosis. One of the main challenges in studying and monitoring MCs is the great structural diversity within the class. The full chemical structure of the first MC was elucidated in the early 1980s and since then, the number of reported structural analogues has grown steadily and continues to do so, thanks largely to advances in analytical methodology. The structures of some of these analogues have been definitively elucidated after chemical isolation using a combination of techniques including nuclear magnetic resonance, amino acid analysis, and tandem mass spectrometry (MS/MS). Others have only been tentatively identified using liquid chromatography-MS/MS without chemical isolation. An understanding of the structural diversity of MCs, the genetic and environmental controls for this diversity and the impact of structure on toxicity are all essential to the ongoing study of MCs across several scientific disciplines. However, because of the diversity of MCs and the range of approaches that have been taken for characterizing them, comprehensive information on the state of knowledge in each of these areas can be challenging to gather. We have conducted an in-depth review of the literature surrounding the identification and toxicity of known MCs and present here a concise review of these topics. At present, at least 279 MCs have been reported and are tabulated here. Among these, about 20% (55 of 279) appear to be the result of chemical or biochemical transformations of MCs that can occur in the environment or during sample handling and extraction of cyanobacteria, including oxidation products, methyl esters, or post-biosynthetic metabolites. The toxicity of many MCs has also been studied using a range of different approaches and a great deal of variability can be observed between reported toxicities, even for the same congener. This review will help clarify the current state of knowledge on the structural diversity of MCs as a class and the impacts of structure on toxicity, as well as to identify gaps in knowledge that should be addressed in future research.

Structural Diversity, Characterization and Toxicology of Microcystins.

Poisoning of sheep in new south wales by the blue-green alga anacystis cyanea (kuetz.) dr. and dail.

Fifty-seven epiphytic species were found to occur on the two sea-grass hosts Zostera and Posidonia in Botany Bay and Jervis Bay, N.S.W. Among the algal epiphytes on Posidonia australis several indicator species were identified and it was found that their relative frequency of occurrence can be used to differentiate sites within the two bays. These indicator species can be used also to classify a collection from an unknown site within the region, and their relative occurrences may provide a useful index for early detection of changes in the bay environments.

A comparative study of epiphytic algal communities on two common genera of sea‐grasses in eastern Australia

A fifty-three metre inter-tidal transect on a headland near Sydney, New South Wales, has been studied. Its profile, fauna and flora are illustrated and described.

Herbivore-Algal relationships on a coastal rock platform (Cape Banks, N.S.W.).

A long-term study (1973-9) was made of the intertidal floras of two headlands, one exposed to the ocean, the other in a bay. Many algal species varied erratically in frequency or occurrence from year to year, apparently due to local chance causes, but in some years many species showed reductions in frequency. In these years the changes in the flora appear to be associated with sand movements, which are possibly due to locally damaging storms. Recovery of the floras follows these depressions, but it is stressed that this recovery depends on the existence of a reservoir of spore-producing plants which in turn depends on the maintenance of good water quality in the sea.



The naturally occurring variations in floras are greater than are any induced by a low volume well-treated sewerage outfall, except in the immediate area of the outfall.

Long‐term variation in algal intertidal floras

Australian literature records stock losses due to excessive growths in water of the cyanophyte algae Anaeystis cyanea (Kuetz.) Dr. and Dail. (= Microcystis aeruginosa Kuetz.), Anabaina circinalis Rabenh. and Nodularia spumigena Mert. (now Nostoc spumigena (Mert.) Drouet). These algal species were recorded in Australia at least sixty years ago, but their increasing occurrence, wide distribution and the resultant damage appear to be due to increasing pollution of the water.

The Occurrence of Toxic Cyanophyte Blooms in Australia

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