Problems associated with Fusarium mycotoxins in cereals. Angelo Visconti ABSTRACT Fungi of the genus Fusarium are common plant pathogens occurring worldwide, mainly associated with cereal crops. Fusarium species can produce over one hundred secondary metabolites, some of which can unfavourably affect human and animal health. The most important Fusarium mycotoxins, that can frequently occur at biologically significant concentrations in cereals, are fumonisins, zearalenone and trichothecenes (deoxynivalenol, nivalenol and T-2 toxin). These compounds have been implicated as the causative agents in a variety of animal diseases, such as leukoencephalomalacia, pulmonary oedema, infertility, diarrhoea, vomiting, anorexia, leukopenia, immunosuppression, skin and gastrointestinal irritation, hemorraging, etc., and have been associated to some human diseases. The IARC working group on carcinogenic risk to humans has classified the toxins derived from Fusarium moniliforme (including fumonisins) as possibly carcinogenic to humans (Group 2B). Fusarium mycotoxins contamination of cereals can cause economic losses at all levels of food and feed production including crop and animal production, crop distribution and processing. Practical strategies to eliminate these mycotoxins from feed and food are required, although some progress is being made at level of individual compound or group of compounds. Health risks associated with the consumption of cereal products contaminated with Fusarium mycotoxins are worldwide recognized and depend on the extent to which they are consumed in a diversified diet; several countries have recommended maximum tolerated levels for some of these mycotoxins. Further risk assessment and regulatory efforts should be established in order to ensure that Fusarium mycotoxins levels in foods and feeds are kept well below of those levels which can constitute a potential hazard for human and animal health. Key words: Fusarium, mycotoxins, biomarkers, trichothecenes, fumonisins, zearalenone.
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Problems associated with Fusarium mycotoxins in cereals.
Angelo Visconti
ABSTRACT
Fungi of the genus Fusarium are common plant pathogens occurring worldwide, mainly associated with cereal crops.
Fusarium species can produce over one hundred secondary metabolites, some of which can unfavourably affect human
and animal health. The most important Fusarium mycotoxins, that can frequently occur at biologically significant
concentrations in cereals, are fumonisins, zearalenone and trichothecenes (deoxynivalenol, nivalenol and T-2 toxin).
These compounds have been implicated as the causative agents in a variety of animal diseases, such as
Istituto Tossine e Micotossine da Parassiti Vegetali, CNR, V.le L. Einaudi 51, I-70125 Bari, Italy
INTRODUCTION
Fungi of the genus Fusarium are common plant pathogens occurring worldwide, mainly associated with cereal crops.
Fusarium species can produce over one hundred secondary metabolites, some of which can unfavourably affect human
and animal health. The most important Fusarium mycotoxins, that can frequently occur at biologically significant
concentrations in cereals, are fumonisins, zearalenone and trichothecenes (deoxynivalenol, nivalenol and T-2 toxin).
These compounds can occur naturally in cereals, either individually or as specific clusters of two or more of them
depending on the producing fungal species (or strain); they have been implicated (alone or in combination between
themselves and/or with other mycotoxins) as the causative agents in a variety of animal diseases and have been
associated to some human diseases. Maize is the crop most susceptible to contamination by all Fusarium mycotoxins
(particularly important are fumonisins), while wheat and barley are subjected to contamination of deoxynivalenol,
nivalenol and, at lesser extent, zearalenone and T-2 toxin and related trichothecenes. The major fungal species (widely
distributed in cereal crops) producing these mycotoxins are F. graminearum, F. culmorum and F. crookwellense,
producing zearalenone, deoxynivalenol, nivalenol and related trichothecenes, F. sporotrichioides, producing T-2 toxin
and related trichothecens, and F. moniliforme and F. proliferatum, producing fumonisins.
Mycotoxin contamination of crops may cause economic losses at all levels of food and feed production including crop
and animal production. Contaminated grains result in increased costs for handlers and distributors due to extra drying
costs, excess storage capacity, losses in transit, loss in markets. The occurrence of mycotoxins varies from commmodity
to commodity, year to year, and region to region. Years of environmental conditions favorable to mycotoxin
development will result in higher economic losses. F. graminearum is the primary causal agent of wheat head scab and
causes extensive damage to wheat in humid and semihumid wheat growing areas of the world by reducing grain yield
and quality.
Although the prevention of mycotoxin contamination of grain is the main goal of food and agricultural industries
throughout the world, under certain environmental conditions the contamination of various cereal grains with Fusarium
fungi and mycotoxins are unavoidable for grain producers. While certain treatments have been found to reduce
concentrations of specific mycotoxins, no single method has been developed that is equally effective against the wide
variety of mycotoxins that may co-occurs in different cereal grains. The ideal decontamination procedure should be
easy to use, inexpensive and should not lead to the formation of compounds that are still toxic or can alterate the
nutritional and palatability properties of the grain or grain products.
This report brings together some general information about toxicity to man and animals of the most important Fusarium
mycotoxins (some details on carcinogenicity, cytotoxicity and immunotoxicity, and acute animal toxicity), the relevant
economic losses and detoxification approaches, and regulatory issues worldwide. Some data from recent investigations
carried out at the CNR Institute of Toxins and Mycotoxins (Bari, Italy) are also presented with particular emphasis to
the use of biomarkers to evaluate human and animal exposure to fumonisins and to in vivo and in vitro assays for
fumonisins detoxification by means of non-nutritive adsorbent compounds.
TOXICITY OF FUSARIUM MYCOTOXINS
Carcinogenicity
The International Agency for Research on Cancer (IARC, 1993) has grouped the main Fusarium mycotoxins on the
basis of the fungal species producing them as it represents the best way to identify the real situation through which
humans become exposed to these naturally occurring toxins. Therefore, the most important mycotoxins, in terms of
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natural occurrence and toxicology, have been grouped in: toxins derived from F. sporotrichioides (T-2 toxin and
related trichotecenes), toxins derived from F. graminearum, F. culmorum and F. crookwellense (Deoxynivalenol,
Nivalenol, Fusarenone X and Zearalenone), and toxins derived from F. moniliforme (Fumonisins and Fusarin C). Only
the group of toxins deriving from F. moniliforme was identified as group 2B, i.e. possible carcinogenic to humans and
with sufficient evidence of carcinogenicity towards experimental animals, whereas the data relevant to the other groups
of toxins or to individual toxins were not sufficient (or adequate) to make them classifiable as to their carcinogenity to
humans (group 3). The following carcinogenicity data were identified by the working group for individual toxins: i) T-2
toxin increased the incidence of pulmonary and hepatic adenomas in mice (additional data from studies with rats were
considered inadequate for evaluation); ii) zearalenone caused an increase in hepatocellular adenomas in female mice
and in pituitary adenomas in both male and female mice; iii) fusarin C induced papilloma or dysplasia in the
forestomach and oesophagus in mice and rats (these data were not considered sufficient to assess the carcinogenicity
towards experimental animals); iv) fumonisin B1 induced hepatocellular carcinoma, cholangiofibrosis and
cholangiocarcinoma in rats (26 month feeding experiment at level of 50 mg/kg); this toxin was shown to be a strong
tumor promoter, but only a weak initiator (similar effects have also been shown for FB 2 and FB3); v) no evidence of
carcinogenicity was observed in mice for deoxynivalenol or nivalenol in feeding experiments lasted 26 weeks or two-
years. The summary of the IARC evaluation of Fusarium mycotoxins (IARC, 1993) is reported in Table 1.
All the above mentioned toxins but fumonisins have shown, at different exent, some genotoxic effect in mammalian
cells in vitro, including clastogenic effects, chromosomal aberrations and sister chromatid exchange, or unscheduled
DNA synthesis, and T-2 toxin induced DNA damage and chromosomal aberration in rodent also in vivo (IARC 1993).
Table 1. Carcinogenicity risk evaluated by IARCa for Fusarium mycotoxins.
Toxins Degree of evidence of carcinogenicitya
Overall evaluationa
In human In animals
Toxins derived from: F. graminearum,F. culmorum, F. crookwellense I Group 3
Zearalenone ND LNivalenol I
Fusarenone X IDeoxynivalenol I
Toxins derived from: F. sporotrichioides ND Group 3
T-2 toxin L
Toxins derived from:F. moniliforme I S Group 2B
Fumonisin B1 LFumonisin B2 I
Fusarin C L*From IARC, 1993a I, insufficient evidence; L, limited evidence; ND, no adequate data; S, sufficient evidence. Group 2B = possibly carcinogenic to humans; Group 3 = not classifiable as to its carcinogenicity to humans.
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Immunotoxic and cytotoxic effects
Fusarium mycotoxins may predispose livestock to infectious disease, and this might result in feed refusal and decreased
productivity. Increased infections in food-producing animals might also result in increased animal-to-human
transmission of pathogens such as Salmonella and Listeria. Ingestion of mycotoxins by humans might contribute to
decreased resistance to infectious agents and neoplasms, and these compounds may function as unrecognized etiological
factor of immune disfunction diseases (Pestka and Bondy, 1994).
The capacity of deoxynivalenol to alter normal immune function is particularly important. There is extensive evidence
that deoxynivalenol can be immunosuppressive or immunostimulatory, depending upon the dose and the duration of of
exposure. While immunosuppression can be explained by the capacity of inhibiting protein synthesis,
immunostimulation can be related to interference with normal regulatory mechanisms. In addition to several
trichothecenes, immunomodulatory effects have been shown for fusarochromanone (TDP-1) and its acetyl derivative
(TDP-2), metabolites of Fusarium equiseti (Minervini et al. 1992).
There are studies showing increased resistance to infections after (oral or intraperitoneal) exposure to both
deoxynivalenol or T-2 toxin (Eriksen and Alexander, 1998). Intraperitoneal preinoculation treatment with T-2 toxin can
be immunostimulatory and can actually enhance resistance to Listeria, whereas postinoculation T-2 toxin treatment is
markedly immunosuppressive. Similarly, enhanced resistance to mastitis pathogens by preinoculation gavage of T-2
toxin or to Staphylococcus hyicus or Mycobacterium avium infections after a single-dose oral pre-treatment with
deoxynivalenol in mice has been observed. However, dietary deoxynivalenol exposures to as low as 2 mg/kg for 5
weeks was sufficient to decrease time-to-death intervals in mice challenged with Listeria; these levels of contamination
can frequently be found in cereal crops when wheater conditions are favourable to the growth of Fusarium in the field
(Eriksen and Alexander, 1998; Pestka and Bondy, 1994).
Zearalenone and its analogues are capable of inhibiting mitogen-stimulated lymphocyte proliferation and can induce
thymic atrophy and macrophage activation (Forsell and Petska 1985, Visconti et al. 1991). Dietary exposure to
relatively high doses (10 mg/kg) of zearalenone for two weeks deacreases resistance to Listeria (Pestka and Bondy,
1994).
Fumonisins have been shown to be cytotoxic to dog kidney and rat hepatoma cell lines. Several studies have shown
altered immune response in poultry fed diets containing fumonisins at relatively high levels (Pestka and Bondy 1994).
Structure-activity relationship of trichothecenes.
The 12,13 epoxy ring, and substitutions of the hydroxyl group or hydrogen in some of the positions of the trichothecene
skeleton influence the cytotoxicity and lymphocyte blastogenesis or protein synthesis inhibition. The toxicity of
trichothecenes varies significantly between different test systems, but the rank order of toxicity between the toxins is
similar. The type A toxins, having a functional group other than carbonyl in C-8 position, have a higher cytotoxic effect
than type B toxins with a carbonyl group in this position, and trichothecenes are in general more cytotoxic than other
Fusarium metabolites. The toxicity of group A toxins decreases in the order of isovaleryl > hydrogen > acetyl >
hydroxyl substituents in the C-8 position, i.e. T-2 toxin > diacetoxyscirpenol > 8-acetyl neosolaniol > neosolaniol. Loss
of side chains in C-4, C-8 or C-15 by hydrolysis of T-2 toxin decreases the toxicity and losses of more than one side
chain in these positions further decreases the toxicity (Visconti et al. 1991). In the type B group, the toxicity is
influenced by the substituents in the C-4 position. In particular, the toxicity decreases in the order of acetyl > hydroxyl
>hydrogen in the C-4 position in the B-type trichothecenes. (Visconti et al. 1991). The presence of a hydroxyl group in
nivalenol increases the toxicity in animals a tenfold as compared to the hydrogen in deoxynivalenol (Eriksen and
Alexander, 1998). Fig. 1 shows the structure activity relationship for 11 type A trichothecenes and 5 type B
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trichothecenes produced by Fusarium with respect to cytotoxicity towards cultured human cell lines (K-562 and MIN-
GL1) as reported by Visconti et al. (1991).
Toxicity towards domestic animals
The main toxic effects of the major Fusarium mycotoxins are reported below.
Zearalenone may be present in cereal crops in cooler and moist regions worldwide. Zearalenone and related
metabolites possess strong estrogenic activity and can result in severe reproductive and infertility problems when they
are fed to domestic animals in sufficient amounts. Swine appears to be the most sensitive of the domestic animal
species, therefore the most frequently reported with problems caused by zearalenone, which include enlargement or
swelling and reddening of the vulva in gilts and sows (vulvovaginitis), swelling of the mammary glands and atrophy of
the ovaries, vaginal and rectal prolapses. In young male it can cause swelling of the prepuce, testicular atrophy,
enlargement of the mammary glands, while in boars it causes reduced libido and a marginal reduction in sperm quality.
Effects in other species are much less pronounced. High concentrations of zearalenone have been associated with
infertility and development of atypical secondary sexual characteristics in heifers (Prelusky et al. 1994).
ammonium hydroxide, have been found to be effective (at different extents) against several Fusarium mycotoxins,
including deoxynivalenol, zearalenone, T-2 toxin, DAS, and fumonisins. In particular sodium bisulfite is one of the
most effective against deoxynivalenol in corn, although the treatment is not suitable for direct application to human
foods. Often chemical treatments have been used in combination with physical treatments to increase the efficacy of
decontamination (Charmley et al. 1995, and references therein).
The administration of T-2 toxin specific antibodies neutralized the in vitro inhibitory effects on protein synthesis in
human B-lymphoblastoid cultures and protected rats from lethal T-2 toxicosis (Feuerstein et al. 1988). Similarly T-2
toxin monoclonal antibodies inhibited human lymphocytes blastogenesis in a specific and dose-dependent manner, with
neutralization occurring in almost equimolar conditions between T-2 and antibody. On this basis a rational for clinical
use of T-2 toxin specific monoclonal antibody in prophylaxis and theraphy of T-2 toxemia has been proposed
(Minervini et al. 1994).
A more appropriate approach to detoxification of mycotoxins involves the use of adsorbent materials with the capacity
to tightly bind and immobilize mycotoxins in the gastrointestinal tract of animals, then reducing the bioavailability of
the toxin. Dietary addition of zeolite, bentonite, or spent bleaching clay from canola oil refining have been shown to
alter the effectof T-2 toxin and zearalenone in rats (CAST 1989).
An extensive review on the prevention of toxic effects of mycotoxins by means of non-nutritive adsorbent compounds
has been published by Ramos et al. (1996), from which the following informations have been taken out with reference
to Fusarium mycotoxins. Cholestyramine has been used to adsorb zearalenone in vitro from gastric and intestinal
simulated fluids. This resin, used extensively for in decreasing total and LDL cholesterol, adsorbed almost 100% of the
mycotoxin present in the medium when used at concentration over 1%. One gram of cholestyramine was able to adsorb
over 1.76 to 2.00 g of zearalenone. Anion exchange resins, such as divinylbenzene-styrene polymers, exhibited
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benficial effects when added to diet of T-2 intoxicated rats; the growth-depressing effect caused by T-2 toxin was
minimized and the reduction in feed consumption was overcome with 5% and 7.5% of resin, respectively. 5% of
divinylbenzene-styrene polymers (anion-exchange) added to diets of rats supplemented with 10 mg zearalenone per 100
g of body weight (2 weeks) resulted in reduced renal and hepatic residues of zearalenone and its metabolites.The
treatment resulted in a major decrease in urinary excretion of conjugated zearalenone and its metabolites. 0.2%
polyvinylpyrrolidone, added to the diets of pigs contaminated with deoxynivalenol (5-14 mg/kg of feed), did not apear
to alleviate the toxic effect of this toxin when fed to barrows and gilts over a period of 5 weeks. Bentonite has been
shown to be effective against T-2 intoxications in rats, but it was ineffective against zearalenone and nivalenol in pigs.
The efficacy of aluminosilicates (HSCAS), which are very effective with regard to preventing aflatoxicoses, was
limited against zearalenone and practically zero for T-2 toxin, diacetoxyscirpenol and deoxynivalenol. Beneficial effects
of activated charcoal have been shown in rats intoxicated with T-2 toxin. Superactivated charcoal (2-3 fold the
absorptive capacity of other leading charcoals) had a beneficial effect (70% survival) on rats intubated with T-2 toxin at
levels 6 fold the LD50. When administered to rats after 3-5 h from having been given a lethal dose of T-2 toxin, it
prevented deaths with the median effective dose being 0.175 g/kg bw. The mechanism of this beneficial effect has been
postulated to be the ability, shown in vitro, of the charcoal to bind the mycotoxin, preventing its absorption and
especially enterohepatic recirculation (Ramos et al. 1996, and references therein).
Alteration of bioavailability of fumonisins by binding agents.
Galvano et al. (1997) identified some commercial activated carbons with high affinity for fumonisin B1 after testing in
vitro several activated carbons to establish the relation of adsorption ability to physicochemical parameters, such as
surface area, iodine number and methylene blue index. Consequently, we have tested one of the most promising of these
materials for its ability to protect rats in vivo from dietary fumonisin toxicity (Solfrizzo et al. 1998a). Rats (four animals
Table 2. Measurements of weight and SA/SO ratio of biological samples from rats exposed to fumonisins through Fusarium moniliforme contaminated diet, with 2% or without activated carbon (AC)
PARAMETERCONTROL DIET
(+2% AC)CONTAMINATED DIET
(4 mg/kg FB1+FB2)REVERSE
DIET*CONTAMINATED DIET + AC
(4 mg/kg FB1+FB2 + 2% AC)
Liver weight (g) 7.27 a** 9.45 b 9.58 b 6.94 a
SA/SO in liver 0.06 a 0.09 a 0.16 b 0.09 a
Kidney weight (g) 0.96 a 1.04 a 1.07 a 0.95 a
SA/SO in kidney 0.19 a 1.10 b 0.15 a 0.88 b
SA/SO in urine 0.37 a 0.41 a 0.27 a 0.38 a
* Rats exposed for one week to fumonisin contaminated diet followed by one week of blank control diet** Data with same letter in individual row represent means of 4 measurements which have no significant difference, while different letters indicate significant difference (P<0.05)
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per group) were fed diets containing 0 or 4 µg/g FB1 + FB2 (alone or in combination with 2% activated carbon) ad
libitum for one week; adequate amounts of fumonisin producing Fusarium moniliforme maize culture were incorporated
into blank control diet to obtain contaminated diets. Urine samples were collected from metabolic cages after one week
feeding; liver and kidney tissues were collected and weighed after sacrifying the animals. The elevation of SA
concentration or SA/SO ratio were used as fumonisins biomarkers. The results of the all experiment are summarized in
Table 2. The organ weights and on the biomarker value in urine and organs are reported to indicate the effects of
fumonisins administration and the (eventual) reverse effects of the washing out (reverse diet) or of the addition of
activated carbon.
Rats exposed to contaminated diet showed statistically significant increase of liver weight (P<0.05, compared to
control) whereas the kidney weight remained costant. The analysis of SA and SA/SO in kidney, liver and urine of
fumonisin treated rats showed statistically significant increase of SA and SA/SO in kidney, and SA in liver. SA mean
concentration and SA/SO ratio in liver and kidney of rats exposed to contaminated diet supplemented with activated
carbon were lower than the corresponding values of rats fed only with contaminated diet, but the differences were not
statistically significant. In contrast, the addition of activated carbon resulted effective (P<0.01) in avoiding the increase
of liver weight caused by the diet containing Fusarium moniliforme maize culture (Solfrizzo et al. 1998a).
The reversibility of fumonisins to elicite the biomarker was investigated in kidney and liver of four rats exposed
consecutively to one week of contaminated diet and one week of blank control diet. Mean values of kidney SA/SO
returned to control values after one week feeding blank control diet. In contrast mean value of SA/SO in liver was
significantly elevated after one week washing out, indicating that the effect of fumonisins on sphingolipid metabolism
in liver last longer than in kidney, although the quantitative effect (increase of SA/SO value) in liver is lesser than in the
kidney. The analysis of SA/SO in urine of treated rats did not give any information as mean values were not statistically
significant from the control values, although in a previous experiment was demonstrated that 2 µg/g of fumonisins were
enough to elicite urinary SA/SO. The disparity of the results between the two experiments could be explained by the
longer exposition to fumonisins used in the previous experiment (see above: biomarkers). In particular the rats were
exposed for 9 days to 0.5 µg/g of fumonisins followed by 13 days to 2 µg/g of fumonisins whereas in this experiment
rats were fed with contaminated diet only for one week.
Several adsorbent materials, namely celite, bentonite, activated carbon and cholestyramine, have been tested in our
laboratory at various fumonisins concentrations to evaluate the in vitro capacity to adsorb fumonisin B1 (Solfrizzo et al.
1998b). Experiments were performed by incubating the sorbent material (1 mg/ml) with increasing concentrations of
fumonisin B1 in water (up to 260 µg/ml). Celite was not effective even at the lowest tested fumonisin concentration (3.2
µg/ml), while bentonite showed a relatively low affinity for fumonisin, with ca. 12% adsorbption from a solution
containing 13 µg/ml FB1. Activated carbon and cholestyramine exhibited a good adsorption capacity even at high toxin
concentrations (62% and 85%, respectively, at FB1 concentration of ca. 200 µg/ml). The adsorption isotherms of
activated charcoal and cholestyramine, shown in Fig. 3, clearly indicated cholestyramine as the best candidate for
testing in vivo the adsorbing potential with respect to FB1. The effectiveness of the binding agent in vivo in rats fed with
fumonisin contaminated diets was evaluated by using the measurements of the SA/SO ratio as biomarker of the
bioavailable fumonisins. The value of the SA/SO ratio decreased significantly (P<0.01), from 2.82 to 1.36, when 2%
of cholestyramine was added to a diet containing 20 µg/g of fumonisins (FB1 + FB2) (Solfrizzo et al. 1998b). This
result demonstrates the beneficial effect of cholestyramine in reducing the bioavalaibility of fumonisins in vivo in rats at
the gastrointestinal level. The effectiveness of this kind of compounds, highly charged quaternary ammonium (strong
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Unadsorbed FB1 concentration (µg/ml)
0 10 20 30 40 50 60 70 80
Ad
sorb
ed F
B1
amou
nt
(µg/
mg)
0
25
50
75
100
125
150
175
200
CholestyramineActivated carbon
Fig. 3. Adsorption isotherms of cholestyramine and activated carbon with respect to fumonisin B1.
anion exchange) resin, could be due to the sum of two factors, the ion exchange capacity of the adsorbent and its
capacity to physically entrap the fumoninins in the polymeric matrix.
PUBLIC HEALTH ASPECTS OF FUSARIUM MYCOTOXINS IN FOOD
Health risks associated with the consumption of cereal products contaminated with Fusarium mycotoxins are
worldwide recognized and depend on the extent to which they are consumed in a diversified diet.
Outbreaks of human intoxications associated with wheat contaminated by F.graminearum and relevant mycotoxins
have been reported in India, China and Japan, with symptoms including nausea, abdominal pain, throat irritation,
Table 3. Worldwide recommended regulatory limits on Fusarium mycotoxins in cereals and cereal products
Country Mycotoxin Commodity Limit ng/g
Austria Deoxynivalenol
Zearalenone
Wheat, rye / durum wheat
Wheat, rye, durum wheat
500 / 750
60
Brazil Zearalenone Maize 200
Canada Deoxynivalenol
Deoxynivalenol
HT-2 toxin
All mycotoxins
Uncleaned soft wheat (food)
Diets for:
swine, young calves, lactating dairy animals
cattle, poultry
swine, young calves, lactating dairy animals
cattle, poultry
Feedstuffs for reproducing animals
2,000
1,000
5,000
25
100
0
France Zearalenone Cereals 200
Hungary T-2, HT-2, DAS,
NIV
Zearalenone
Deoxynivalenol
“
“
Flour and muesli
“ “
“ “
bran for meal
cereals
300
100
1,000
1,200
2,000
Israel T-2 toxin Grain for feed 100
Netherlands All mycotoxins Cereal(product)s 0
Romania Zearalenone All foods 30
Russia T-2 toxin
Zearalenone
Cereals (wheat hard and stron type), flour,
wheat bran
“ “ “ “ “ “
100
1,000
Switzerland Fumonisins
B1+B2 Maize (products) 1,000
Uruguay Zearalenone Maize, barley 200
U.S.A. Deoxynivalenol
“ “
Fumonisins
Finished wheat products (food)
Grains and grain by-products for feed
Maize (products) for feed
1,000
5,000-10,000*
5,000- 50,000**
From: FAO 1997, Eriksen and Alexander 1998* 5,000 : not exceeding 40% of the diet, destined fir swine (not exceeding 40% of the diet); 10,000: destined for ruminating beef and feed lot cattle older than 4 mos and for chicken (not exceeding 50% of the cattle or chicken total diet).**feed destined to horses (5,000), pigs (10,000), beef cattle and poultry (50,000)
diarrhoea, dizziness and headaches (Beardall and Miller 1994). In China several thousands people have been recorded
as victims of outbreaks attributed to the consumption of scabby wheat and moldy maize; typically, people became ill
from 5 to 30 min after consumption; deoxynivalenol and zearalenone at doses considered toxic were found in samples
of the incriminated food. An outbreak of disease affecting about 50,000 people in the Kashmir Valley (India) was
attributed to the consumption of bread made from rain-damaged wheat; the wheat associated to mild gastrointestinal
tract symptoms was reported to contain several trichothecenes. Pre-puberty was observed in children in Puerto Rico,
possibly caused by zearalenone ingestion (Beardall and Miller, 1994).
Alimentary toxic aleukia has been widely reported in the former U.S.S.R. since 1913 and has been attributed to the
consumption of grain contaminated with Fusarium fungi, which have been shown to produce trichothecenes (T-2 toxin
and other type A trichothecenes). The most severe outbreak occurred in the spring of 1944 in the Orenburg district, in
which 10% of the population were affected and mortality rates were as high as 60% in some counties. Clinical features
of the disease include leukopenia, agranulocytosis, bleading from the nose, throat, and gums, necrotic angina, a
hemorragic rash, sepsis, exhaustion of the bone marrow, and fever (Beardall and Miller, 1994).
The oesophageal cancer has been somewhat associated with the maize infected by Fusarium moniliforme and/or
Fusarium graminearum and relevant mycotoxins (fumonisins or trichothecenes and zearalenone) in some regions of
South Africa and China (Beardall and Miller, 1994). Home-grown maize in certain rural areas can be contaminated at
>100 g/g, like Transkei region in South Africa, and Linxian and Cixian counties in China. In some of these areas the
consumption of maize contaminated at high levels of fumonisins has been associated with a high incidence of human
oesophageal cancer (Marasas 1995). High levels of fumonisins (up to 20 µg/g) have also been found in maize based
food (maize, maize flour and polenta) in Italy. Increased human consumption of maize meal in certain regions of Italy
has also been associated with increased risk of oesophageal cancer compared to other parts of the country and western
Europe, although a direct causal role for fumonisins in the aetiology of such tumors has not been established (Visconti
et al. 1998).
The hazards of Fusarium mycotoxins to the human and animal health have lead government authorities of several
countries to recommend regulatory limits for the presence of some of these mycotoxins in several cereal based foods or
feeds (see Table 3).
The Nordic Council of Ministers has recently published a monograph for the risk assessment of Fusarium toxins in
cereals which reports the temporary tolerable daily intake (tTDI) of some of these mycotoxins for the population of the
Scandinavian countries (Eriksen and Alexander 1998). A summary of the report is presented in Table 4.
Tolerable daily intakes (TDIs) of fumonisin B1 in the Netherlands, based on a safety factor of 100, have been calculated
as following: 500 and 2300 ng/kg bw based on the no observed effect levels (NOELs) estimated in toxicity studies in
rats with purified FB1 administered by gavage and amended food, respectively, and 1000 ng/kg bw derived from FB1
related toxic effects observed in horses (de Nijs 1998). The exposure estimate for the Netherlands was 4, 57, and 220 µg
FB1/day/person based on consumption of 3, 42, and 162 g of maize and a mean FB1 content of 1.36 mg/kg in the maize (de
Nijs 1998). It was estimated that from the group at risk, people with gluten intolerance such as people with celiac or
Duhring’s disease (0.02 % of the entire population), 37% is daily exposed to an intake of > 100 µg FB1 and 97% to levels
of > 1 µg FB1 per person, whereas for all people these percentages would be 1% and 49%, respectively (de Nijs 1998).
Human exposure estimates or risk assessment have been proposed for fumonisins in other countries including Switzerland,
Canada, South Africa, U.S.A.. The results of these risk assessments (depending on safety/uncertainty factors chosen)
indicate a range of possibilities from very low risk in Canada (<0.089 µg/kg bw/day over the period 1991-1995) to a very
high risk in subsistence farmers on a maize staple diet in parts of rural South Africa. Estimates of human exposure in the
Transkei, South Africa, ranged from 14 to 440 mg/kg b.w./day, varying considerably according to the source and extent of
maize in the diet as well as the extent of Fusarium kernel rot prevalent in the harvested crop. These illustrate the
considerable impact of differing maize consumption patterns by different population groups (Marasas, 1997).
Table 4. Critical effect in animal studies, established temporary tolerable daily intake (tTDI) and estimated average Scandinavian intake of some Fusarium toxins.*
Toxin Critical effect in animal
studies (µg/kg bw)
Proposed tTDI
(µg/kg bw)
Uncertainty factor
used in the assessment
Average Scandinavian
intake (µg/day)
T-2 / HT-2 toxins 100-200a 0-0.2 1000 0.14-0.20
DON 50b; 100c 0-1 100 0.4 - 0.7
NIV 0.05 -0.09
ZEN 50d; 16000a 0 -0.1 (matematical extrapolation witha risk level of 10-6)
0.02
FB1 <1000e; 3500a <1 not estimated
*From: Eriksen and Alexander, 1998a proliferative/carcinogenic effect; bvomiting; cgeneral and immunotoxic effect; dhormonal/reproductive effect; eliver/brain damage
CONCLUSIONS
Trichothecenes, zearalenone and fumonisins are distributed widely in cereal crops, to the extent of ubiquity in certain
crops grown in specific regions and seasons. During seasons of extensive mycotoxin contamination, grain shortages
may occur leading to elevate prices and costs for livestock and poultry producers and consumers of grain products.
Most economic losses due to the consumption of mycotoxin-contaminated diets by farm animals result from reduced
animal production and increased disease incidence. Immunosuppression with its associated increases in infection and
disease incidence also increases production costs. Animal diseases such as infertility, vaginal or rectal prolapse,
anorexia, skin and gastrointestinal irritation, haemorraging, abnornal offsprings, leukoencephalomalacia, pulmonary
edema, liver tumours, etc. could be ascribed to the consumption of feed contaminated with these mycotoxins.
Many approaches have been used to reduce the toxicity of mycotoxin contaminated feed. However, most methods have
been tested on a limited number of specific toxins. Since contaminated cereals may contain a broad range of mycotoxins
of differing chemical characteristics, including heat stability, solubility, and adsorbent affinity, a detoxification
procedure that works well for individual toxins may not be effective for the diverse mycotoxin combinations that occur
naturally.
Health risks associated with the consumption of cereal products contaminated with Fusarium mycotoxins are
worldwide recognized and depend on the extent to which they are consumed in a diversified diet. To some extent, the
presence of small amounts of Fusarium mycotoxins in cereals and related food products is unavoidable; this
necessitates risk assessments carried out by regulatory bodies in several countries to help establish regulatory guidelines
to protect public health. By assessing the levels in food at which these substances may pose a potential risk to human
health, it is possible to devise appropriate risk management strategies. However, several important factors have to be
taken into account in making a rational risk management decision, including adequate toxicological data and knowledge
of the level of exposure, availability of technically sound analytical procedures (including sampling), socioeconomic
factors, food intake patterns and levels of mycotoxins in food commodities which may vary considerably between
countries.
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