Fatty acid composition of bacteria associated with the toxic dinoflagellate Ostreopsis lenticularis and with Caribbean Palythoa species.

The fatty acid composition of a Pseudomonas sp. (Alteromonas) and its host, the dinoflagellate Ostreopsis lenticularis, vectors in ciguatera fish poisoning, has been studied. The major fatty acids in O. lenticularis were 16:0, 20:5n-3, and 22:6n-3, but 18:2n-6, 18:3n-3, and 18:n-3 were also identified. In contrast to other dinoflagellates, 1 8:5n-3 was not detected in O. lenticularis. Even-chain fatty acids such as 9-16:1, 11-18:1, and 13-20:1 predominated in the Pseudomonas sp. from O. lenticularis, but 1 6-20% of (E)-11-methyl-12-octadecenoic acid was also identified. The chirality of the latter was confirmed by total synthesis (28% overall yield) starting from oxacyclotridecan-2-one. The fatty acid compositions of two other Pseudomonas species, from the palytoxin-producing zoanthids Palythoa mamillosa and P. caribdea, were also studied and were similar to that of the Pseudomonas sp. from O. lenticularis. The possibility of using some of these fatty acids as chemotaxonomic lipids in identifying marine animals that consume toxic dinoflagellates or zoanthids is discussed.

Origin and transfer of toxins involved in ciguatera.

1. Ciguatera is a disease caused by sodium channel activator toxins and results from the consumption of warm water fish contaminated by the ciguatoxin class of polyether toxins. 2. Other toxins, including okadaic acid and maitotoxin, have no proven role in causing human illness associated with ciguatera. 3. Ciguatera often affects only a discrete region of a reef, with flare-ups of ciguatera being both temporally and spatially unpredictable. 4. The ciguatoxins likely arise through the biotransformation and acid-catalysed spiroisomerisation of gambiertoxin-4A produced by Gambierdiscus toxicus and it is unlikely that other toxic benthic dinoflagellates are involved. 5. Events leading to a ciguatera outbreak are initiated by environmental and genetic factors that favour the proliferation of gambiertoxins, with an apparent role for anthropomorphic effects; however, the precise factors involved are yet to be determined. 6. The gambiertoxins and/or ciguatoxins are transferred from the benthos to herbivorous species (fish, invertebrates etc) and then to carnivorous fish via marine food chains. 7. Factors influencing the concentration of ciguatoxins that accumulate in fish include the rate of dietary intake, the efficiency of assimilation, the degree and nature of any toxin biotransformation, the rate of depuration, and the rate of growth of fish.

Progress on chemical knowledge of ciguatoxins.

The chemical data setted up on the ciguatoxins responsible for ciguatera fish poisonings are summarized and discussed. The multiplicity of the toxic compounds isolated from fish and algal material is described. A tentative screening of the principal toxins still on process in the two laboratories has shown that (1) CTX is dominant in carnivorous fish, (2) less polar toxins are dominant in herbivorous fish, (3) CTX precursors are produced by G. toxicus in natura and in culture conditions. The increasing polarity of the toxins in step with the food chain levels supports the hypothesis of an oxidative modification of the precursors during the bio-accumulation in fish.

Toxicity of French Polynesian strains of Gambierdiscus toxicus in cultures.

Seven clonal strains of Gambierdiscus toxicus isolated from three ciguateric areas around Tahiti island were mass cultured and extracted for ciguatoxins and maitotoxin. CTX analogs were detected only in one clone (GTP1), suggesting that CTX production may be strain-dependent. However, this in vitro production of CTXs, which remains fairly poor with regards to the toxicity levels encountered in wild G. toxicus, is not a stable temporal characteristic. On the other hand, maitotoxic compounds were detected in all 7 strains in copious amount, especially in clone GTH2.

Strain dependent production of ciguatoxin precursors (gambiertoxins) by Gambierdiscus toxicus (Dinophyceae) in culture.

Thirteen strains of Gambierdiscus toxicus isolated from Queensland (Australia), Hawaii, French Polynesia and the Virgin Islands were mass cultured and extracted for ciguatoxin. A biodetrital sample containing wild G. toxicus collected from the Republic of Kiribati was also extracted for ciguatoxin. Ciguatoxin, as characterized from moray eels, was not detected in any of the strains examined. Two Queensland strains and the wild G. toxicus produced putative ciguatoxin precursors named gambiertoxins. These gambiertoxins were less polar than ciguatoxin but produced bioassay signs in mice and in-vitro responses in isolated guinea pig atria and vas deferens which were similar (but not identical) to those produced by ciguatoxin. The gambiertoxins from cultured cells were also shown to competitively inhibit the binding of [3H]brevetoxin-3 to rat brain membranes in a dose-dependent manner. The gambiertoxins were more potent than ciguatoxin (on a per mouse unit basis) at stimulating neural elements of guinea pig atria. The two culture strains produced similar amounts of gambiertoxins, even when grown in nutrient media made from different seawater containing different concentrations of nutrients. Changes in nutrient media did not induce the other strains of G. toxicus to produce gambiertoxins. The production of these ciguatoxin precursors appears to be limited to only certain genetic strains of G. toxicus, with the majority of strains not producing these toxins. We propose that ciguatera occurs when blooms of G. toxicus strains genetically capable of producing these ciguatoxin precursors enter the marine food chain. These toxins could then become oxidatively metabolized in fishes to the major polar ciguatoxin. Wild cells produced approximately 100-fold greater quantities of gambiertoxins per cell than did the two culture strains indicating that there is considerable potential for increased production of these ciguatoxin precursors from G. toxicus in culture.