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IARC MONOGRAPHS ON THE EVALUATION OF CARCINOGENIC ...

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322<br />

<strong>IARC</strong> <strong>M<strong>ON</strong>OGRAPHS</strong> VOLUME 82<br />

observed in horses and ponies after ingestion of feeds naturally contaminated with fumonisins<br />

at low concentrations (Wilson et al., 1992; Ross et al., 1993). The development of<br />

brain lesions in the absence of major liver lesions does not preclude a contribution of biochemical<br />

dysfunction in non-brain tissue to the development of brain lesions. Length of<br />

exposure, level of contamination, individual animal differences, previous exposure or<br />

pre-existing liver impairment may all contribute to the appearance of the clinical disease<br />

(Ross et al., 1993).<br />

The lowest dietary dose observed to induce ELEM was 22 mg/kg fumonisin B 1<br />

in a diet formulated with naturally contaminated maize screenings: one pony died of<br />

ELEM after consumption of contaminated diet for 235 days, of which the final 55 days’<br />

diet contained 22 ppm fumonisin B 1 (Wilson et al., 1992). Analysis of feeds from<br />

confirmed cases of ELEM indicated that consumption of feed with a fumonisin B 1 concentration<br />

greater than 10 mg/kg diet is associated with increased risk of development of<br />

ELEM, whereas a concentration less than 6 mg/kg is not (Ross et al., 1994). The minimum<br />

toxic dose of pure fumonisins is unknown.<br />

In swine, fumonisin B 1 causes damage to the liver, lungs and cardiovascular and<br />

immune systems. Liver lesions have been induced with fumonisin-contaminated maize<br />

screenings at 1.1 mg/kg per day (fumonisins B 1 and B 2; 17 mg/kg fumonisin B 1 and<br />

6 mg/kg fumonisin B 2 in the diet). Intravenous exposures resulted in changes similar to<br />

those recorded in rodents including necrosis and cell proliferation (Motelin et al., 1994;<br />

Haschek et al., 2001). When pure fumonisin B 1 was fed to Yorkshire swine at dietary<br />

levels of 0.1, 1 or 10 mg/kg (0.005, 0.052 or 0.496 mg/kg bw), apart from reduced organ<br />

weights (pancreas, adrenals), no histopathological signs of organ damage were observed.<br />

There were changes in sphingolipid ratios in lung, liver and kidney at the highest dose,<br />

as well as increased serum cholesterol (Rotter et al., 1996). Fumonisin B 1 given to young<br />

adult swine at several doses up to 1 mg/kg in the diet resulted in changes in serum cholesterol<br />

and in altered carcass fat distribution at 0.05 mg/kg bw (Rotter et al., 1997).<br />

Lung oedema occurs in pigs following very high fumonisin B 1 exposure (≥<br />

100 ppm in diet, or ≥ 16 mg/kg bw per day). Clinical signs of lung oedema typically<br />

occur 2–7 days after exposure, and usually include dyspnoea, weakness, cyanosis and<br />

death (Osweiler et al., 1992; Haschek et al., 2001). At necropsy, the animals exhibit<br />

varying degrees of interstitial and interlobular oedema, with pulmonary oedema and<br />

hydrothorax, with varying amounts of clear yellow fluid accumulating in the pleural<br />

cavity (Colvin & Harrison, 1992; Colvin et al., 1993). Fumonisin B 1 is believed to be a<br />

negative osmotropic agent causing decreased cardiac contractility. It has been hypothesized<br />

that the cardiovascular alterations are a consequence of sphingosine-induced<br />

inhibition of L-type calcium channels. Pulmonary oedema results from left-sided heart<br />

failure (Smith et al., 1996, 2000; Haschek et al., 2001). Porcine pulmonary oedema was<br />

produced within 3–4 days after pigs started consuming a diet of culture material that<br />

provided 20 mg/kg bw fumonisin B 1 per day (Smith et al., 1999). There are no published<br />

studies on pulmonary oedema induced by oral exposure to pure fumonisin B 1.

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