• Korean Journal Plant Pathology
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• v.11 no.4
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• pp.318-323
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• 1995

The effect of AF-toxin I produced by the strawberry pathotype of Alternaria alternata on the protein synthesis of susceptible strawberry protoplasts was examined by using the radiolabeled amino acids. The incorporation of the radiolabeled amino acids into newly synthesized proteins in the strawberry protoplasts was stimulated by the toxin treatment at relatively low concentrations (2.2$\times$10-11 to 2.2$\times$10-9 M), but not at higher concentrations (2.2$\times$10-8 to 2.2$\times$10-6 M). An one-dimensional SDS-polyacrylamide gel electrophoresis revealed no detectable differences in the proteins synthesized in both the toxintreated and untreated protoplasts. The susceptible strawberry protoplasts were treated with AF-toxin I and stained with Fluostain I to detect the extracellular polysaccharides. The toxin treatment induced the accumulation of extracellular polysccharides in a dose-dependent manner. These results indicate a transient activation of cellular metabolism in the susceptible cells by the toxin exposure.

• Asian-Australasian Journal of Animal Sciences
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• v.16 no.7
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• pp.1015-1019
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• 2003

A 50 day feeding trial was conducted with White Leghorn (WL) laying hens, 42 weeks old, to determine if feeding of varying levels of aflatoxin (AF), ochratoxin A (OA) or their combinations has any effect on their performance and egg quality parameters. Feeding of $T_4$, $T_7$, $T_8$, $T_9$ and $T_10$ caused significant reduction in feed intake of hens. Hen day egg productions were significantly reduced at all the levels of toxins except 0.5 ppm of AF. Maximum reduction in egg production was noticed at 2 and 4 ppm of AF and OA, respectively. Average body weight and egg weight were not affected by toxin feeding. The feed efficiency in terms of net feed efficiency and feed consumed per dozen egg produced was significantly reduced at higher levels of both the toxins and their combinations. Feed consumption for production of 1 kg egg mass remained uninfluenced due to aflatoxin feeding whereas significant increase in the value of the same was noticed at 4 ppm level of OA and combination of 1 and 2 ppm of AF and 2 and 4 ppm of OA ($T_9$ and $T_10$), respectively. Various levels of OA (1-4 ppm) and all the combination of two toxins ($T_8$, $T_9$ and $T_10$) significantly altered the shape index of eggs in laying hens. The shell thickness was significantly reduced by higher level of AF (2 ppm), OA (2 and 4 ppm) and their combination. Albumen index, Haugh Unit and yolk index remained unchanged due to incorporation of toxins in the diet. It is concluded that AF, OA either singly or in combination at higher levels could depress the performance in terms of egg production and feed efficiency significantly. The egg quality parameters i.e. shape index and shell thickness were also significantly affected.

• Journal of Marine Bioscience and Biotechnology
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• v.12 no.2
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• pp.108-114
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• 2020

A variety of shellfish species sold for human consumption are available for purchase in the domestic fish market. The microalgae families inhabit the ocean, where planktons supply the main nutritional resource for the growth of shellfish. Some phytoplanktons produce toxic compounds that are accumulated in shellfish and ultimately cause toxicity in humans. This article reports the cytotoxicity of commercially available shellfish species. Accordingly, hot water extract (HWE) and an aqueous fraction of 50% methanol extract (MEE-AF) showed no significant cytotoxicity on the two cell lines (i.e., HL-60 and Vero cell lines), but 50% methanol extract (MEE) in 3, 6 samples showed 50% cytotoxic effects on HL-60 cells, and 1, 4 samples showed 40%, 20% cytotoxic effects on Vero cells, respectively. In addition, their consequential dichloromethane fractions (MEE-DF) exhibited significant toxicities at the highest concentration (1,000 ㎍/ml) on HL-60 and Vero cells. Since the shellfish samples showed cytotoxicity in the dichloromethane fraction, it is possible that the dichloromethane fraction contains marine toxins. Further research will be needed to identify the toxic components from each sample.