William P. Norred

Fumonisin inhibition of de Novo sphingolipid biosynthesis and cytotoxicity are correlated in LLC-PK1 cells

Fumonisins are a group of structurally related compounds produced by Fusarium moniliforme. Recently, it has been shown that fumonisins B1 and B2 are the first naturally occurring inhibitors of sphingosine and sphinganine N-acyltransferase (ceramide synthase) in rat primary hepatocytes (Wang et al. J. Biol. Chem. 266, 14, 486-14, 490, 1991). These enzymes are key components in the pathways for de novo sphingolipid biosynthesis and sphingolipid turnover. The results of the present study show that fumonisins B1 and B2 inhibit proliferation and are cytotoxic to LLC-PK1 cells. Concentrations of fumonisin B1 and B2 between 10 and 35 microM inhibited cell proliferation, whereas higher concentrations (greater than 35 microM) killed cells. Inhibition of cell proliferation and cell death were preceded by a lag period of at least 24 hr during which cells appeared to be functioning normally. Cells exposed to fumonisin B1 exhibited normal growth kinetics and morphology soon after fumonisin B1 was removed; thus, the effects of fumonisin B1 were reversible. The EC50 for alterations in sphingolipid biosynthesis was 10 to 15 microM. Inhibition of de novo sphingolipid biosynthesis occurred before inhibition of cell proliferation or cytotoxicity, and the dose response for the decrease in the [3H]sphingosine to [3H]sphinganine ratio at 7 hr closely paralleled the dose response for effects on proliferation and cytotoxicity at 3-5 days. In addition, the level of free sphinganine, and to a lesser extent sphingosine, increased in fumonisin-treated cells in a dose-dependent manner. During the 24-hr lag period preceding inhibition of cell proliferation, the free sphinganine content increased by 12,800% in cells exposed to 35 microM fumonisin B1. Whereas a mechanistic relationship between the inhibition of de novo sphingolipid biosynthesis and inhibition of proliferation and cell death has not been demonstrated, the results of this study support the hypothesis that inhibition of de novo sphingolipid biosynthesis is an early event in the toxicity of fumonisins to LLC-PK1 cells.

Toxicity and Role of Fumonisins in Animal Diseases and Human Esophageal Cancer

Fumonisins are secondary metabolites of Fusarium moniliforme , Fusarium proliferatum and several other Fusaria that commonly contaminate corn. Only recently discovered in 1988, these mycotoxins appear to be the causative agents of several toxicoses in animals that result from ingestion of moldy corn or corn-based feeds. The syndromes observed vary considerably among the different species affected and include brain lesions in equids, lung edema in swine, and nephrotoxicity, hepatotoxicity and hepatocellular carcinoma in laboratory rats. There is also evidence that suggests that F. moniliforme and fumonisins may also be responsible for esophageal cancer in humans in certain areas of the world where moldy corn is frequently consumed. Studies are currently underway to determine the extent of the hazards posed by fumonisins, and whether controls in the form of regulatory action levels may be necessary.

In vitro toxicology of fumonisins and the mechanistic implications

The effects of fumonisins B1FB1, B2(FB{2}), and the backbone of fumonisin B1 remaining after hydrolysis of the tricarballylic groups with base (HFB1) on sphingolipid biosynthesis were studied in both primary rat hepatocytes and pig kidney epithelial cells (LLC-PK1). Fumonisins were potent inhibitors of sphingolipid biosynthesis in hepatocytes (IC50 of FB1=0.1 μM), but overt toxicity was not observed. In renal cells, fumonisins also inhibited sphingosine biosynthesis (IC50 for FB1=35 μM), and caused decreased cell proliferation as well. Higher doses (⩾70 μM) killed renal cells after exposure for 3 days. The inhibition of de novo sphingolipid biosynthesis was specific, and appeared to be at the site of ceramide synthase, which catalyzes the formation of dihydroceramide or ceramide by the addition of the amide-linked fatty acid to sphinganine or sphingosine. These results may account for the ability of fumonisins to cause equine leucoencephalomalacia and to promote tumor formation.

Effects of selected secondary metabolites of Fusarium moniliforme on unscheduled synthesis of DNA by rat primary hepatocytes

The Fusarium moniliforme mycotoxins--fusarin C, fumonisin B1, moniliformin and bikaverin--were evaluated for genotoxicity by their ability to induce unscheduled DNA synthesis (UDS) in primary rat hepatocytes. Isolated hepatocytes were exposed to several concentrations of moniliformin (5.0-500 microM), bikaverin (1.0-500 microM), fumonisin B1 (0.5-250 microM), or fusarin C (1.0-100 microM). Aflatoxin B1, a known inducer of UDS, was included as a positive control. UDS was determined by autoradiography of cells after their exposure to [3H]thymidine. The highest doses of fusarin C and bikaverin caused cell death, but no cytotoxicity was observed in cells exposed to moniliformin or fumonisin B1. Fumonisin B1, moniliformin and bikaverin were not genotoxic in the UDS assay. The results of the UDS assay with fusarin C were inconclusive since a marginal effect on UDS was obtained.

Comparative studies of hepatotoxicity and fumonisin B1 and B2 content of water and chloroform/methanol extracts of Fusarium moniliforme strain MRC 826 culture material.

Fusarium moniliforme has been associated with several diseases including equine leukoencephalomalacia, human esophageal cancer and hepatotoxicity/hepatocarcinogenicity in laboratory animals. The potential health risks to animals and humans posed by F. moniliforme contaminated grains cannot be assessed until the toxins are identified and toxicologically evaluated. As part of a systematic approach to identifying the hepatotoxins produced by F. moniliforme, diets containing aqueous and chloroform/methanol (1∶1) extracts of F. moniliforme strain MRC 826 culture material (CM) and/or the extracted CM residues were fed to male Sprague-Dawley rats for four weeks. Serum alanine aminotransferase, aspartate aminotransferase and alkaline phosphatase activities were increased after two and four weeks and microscopic liver lesions were found in those animals fed aqueous CM extract and the CM residue after chloroform/ methanol extraction. Fumonisins B1 and B2 were extracted from the CM by water, but not chloroform/ methanol, and were present in the toxic diets at concentrations of 93–139 and 82–147 ppm, respectively. Nontoxic diets contained ≤ 22 ppm fumonisin B1 and ≤65 ppm fumonisin B2.

Effectiveness of ammonia treatment in detoxification of fumonisin-contaminated corn.

Corn throughout the world is frequently contaminated by the fungus Fusarium moniliforme, which produces toxic fumonisins. Ammonia has been shown to detoxify effectively aflatoxins in corn and cottonseed. Since corn can be contaminated by both fumonisins and aflatoxins, we investigated the effects of ammoniation of corn either cultured with or naturally contaminated by F. moniliforme. Fumonisin B1 levels in the culture material and in naturally contaminated corn were reduced by 30 and about 45%, respectively, by the ammonia treatment. Despite the apparent reduction in fumonisin content, the toxicity of the culture material in rats was not altered by ammoniation. Reduced weight gains, elevated serum enzyme levels and histopathological lesions, typical of F. moniliforme toxicity, occurred in rats fed either the ammoniated or non-ammoniated culture material. Atmospheric ammoniation of corn does not appear to be an effective method for the detoxification of F. moniliforme-contaminated corn.

Toxic interaction of fumonisin B1 and fusaric acid measured by injection into fertile chicken egg

Toxic interactions of fusaric acid and fumonisin B1, two mycotoxins produced byFusarium moniliforme, were studied in the chicken embryo. The yolk sacs of fertile White Leghorn eggs were injected before incubation with separate and combined solutions of either fusaric acid and or fumonisin B1. The toxins were administered in either a sterile 10 mM buffered phosphate solution, pH 6.90, which produced a final pH of 6.6 ± 0.2, or sterile distilled water. Toxicity was based on absence of egg pip at the end of the 21-day incubation period. Toxins administered in the phosphate buffer solution were more toxic than those administered in distilled water. When both toxins were combined in equal concentrations and injected into eggs, increased toxicity resulted. Fusaric acid was shown to be a mild toxin to the eggs and when a relatively nontoxic concentration of it was combined with graded doses of fumonisin B1, a synergistic toxic response was obtained. Fusaric acid is only moderately toxic to the chicken egg, however its co-occurrence with other fusaria toxins found on corn and other cereals might present possible antagonisms or synergisms. The results of this egg model suggest that fusaric acid might play a role in enhanced and unpredicted toxicity in mammalian systems if it is consumed with other mycotoxins.

In vivo effects of fumonisin B1-producing and fumonisin B1-nonproducing Fusarium moniliforme isolates are similar: Fumonisins B2 and B3 cause hepato- and nephrotoxicity in rats

Fumonisins are mycotoxins produced by Fusarium moniliforme, F. proliferatum, and related Fusarium species found on corn. They occur naturally in corn-based feeds and foods and are suspected human esophageal carcinogens. Fumonisin B1 (FB1), the most common homologue, causes the animal diseases associated with F. moniliforme. Hepato- and nephrotoxicities, disrupted sphingolipid metabolism, and liver cancer have been found in rats fed FB1. To determine the in vivo effects of diets containing fumonisins B2 (FB2) or B3 (FB3), male rats were fed culture materials (CM) of FB1 non-producing F. moniliforme isolates to provide low (4.6–6.7 ppm), mid (32–49 ppm) or high (219–295 ppm) dietary levels of either FB2 (FB2CM) or FB3 (FB3CM). Other groups were fed culture material of an FB1 producing isolate (FB1CM) providing 6.9, 53 or 303~ppm total fumonisins (FB1 : FB2 : FB3 = 1.0 : 0.38 : 0.15) and a tenth group was fed a control diet having no detectable fumonisins. One-half (n = 5/group) the animals were killed after three weeks, at which time the toxicological and histopathological effects of the three culture materials were similar, mimicked the effects of FB1, and included decreased body weight gains, serum chemical indicators of hepatotoxicity, decreased kidney weights, and apoptosis of hepatocytes and kidney tubular epithelium. FB1CM, FB2CM, and FB3CM affected sphingolipids, causing increased sphinganine to sphingosine ratios (Sa/So) in both liver and kidneys. The remaining animals (n = 5/group) were fed a control diet for three additional weeks. All body weight and tissue specific effects, including increased Sa/So, induced by the FB2CM, FB3CM and low level FB1CM diets were absent following the recovery period. Except for mild biliary lesions found in the high dose FB1CM group and a few apoptotic hepatocytes present in one mid- and two high-dose FB1CM rats, no evidence of toxicity remained in these groups following the recovery period.

Toxicity of the mycotoxin, cyclopiazonic acid, to Sprague-Dawley rats

Groups of male Sprague-Dawley rats received po doses of cyclopiazonic acid (CPA) on four consecutive days at 0.0, 0.2, 2.0, 4.0, or 8.0 mg kg-1 days-1. Clinical signs of toxicity were observed only in the two highest dose groups. Rats in the highest dose group exhibited abnormal behavior, diarrhea, and other signs of toxicity after several days of dosing, and most were moribund before the last scheduled dose was administered. Liver and spleen were more severely affected than other organs in the two highest dose groups. Livers contained diffuse pycnotic nuclei and, in some high-dose rats, focal areas of coagulative necrosis. In the high-dose group aspartate and alanine aminotransferase activities were elevated, cytochrome P-450 concentration was decreased, and glutathione S-transferase activity was unchanged. Spleens were hemorrhagic and white pulp contained necrotic lymphocytes. White cell counts were decreased in a dose-related manner in the two highest dose groups. The gastrointestinal tract of high-dose rats contained pycnotic nuclei, and sites of necrosis were observed in stomach, but these lesions were limited to several animals, and were generally mild. Pathologic changes in conjunction with decreased feed and water intake probably contributed to the general deterioration of high-dose rats that resulted in death.

Studies on the reproductive effects of fusarium moniliforme culture material in rats and the biodistribution of [14c]fumonisin B1 in pregnant rats

Fumonisins are mycotoxins produced by Fusarium moniliforme and other Fusarium species. They are commonly found in corn and corn-based foodstuffs. Fumonisins inhibit sphingolipid (SL) biosynthesis, alter cellular SL profiles, and thus may affect cell proliferation and differentiation, both of which are important processes for reproduction. However, there are few reports of the effects of F. moniliforme or fumonisins on mammalian reproduction or development. To study the reproductive effects of this fungus, diets formulated with culture material of toxic F. moniliforme strain MRC 826 (CM) to provide 0, 1, 10, or 55 ppm fumonisin B1 (FB1) were fed to male and female rats beginning 9 and 2 weeks before mating, respectively, and continuing throughout mating, gestational, and lactational phases of the study. CM caused nephropathy, typical of FB1, in males fed > or = 10 ppm and females fed 55 ppm FB1. No significant reproductive effects were found in males (n = 12/group), dams, and fetuses examined on gestation day 15 (G15) (n > or = 8/group), or dams and litters through day 21 postpartum (n > or = 9/group). Litter weight gain in the 10 or 55 ppm FB1 groups was slightly decreased; however, gross litter weight and physical development of offspring were not affected. Altered SL ratios indicative of fumonisin exposure, specifically increased sphinganine to sphingosine ratios, were found in the livers of dams from the 55-ppm FB1 group on G15. However, SL ratios of abdominal slices, containing liver and kidney, of fetuses from control and high-dose litters did not differ. In a second experiment, two dams were injected intravenously on G15 with 101 micrograms [14C]FB1 (3.179 x 10(5) dpm). After 1 hr, which allowed for ca. 98% of the dose to be cleared from the maternal blood, negligible amounts of radioactivity were found in the fetuses. Together, these results indicate that the CM, and by inference FB1, did not have significant reproductive effects at doses which are minimally toxic, and further suggest that little in utero FB1 exposure occurred through G15.