- freely available
Toxins 2013, 5(3), 504-523; doi:10.3390/toxins5030504
Abstract: The development of liquid chromatography-mass spectrometry (LC-MS)/mass spectrometry (MS) methods for the simultaneous detection and quantification of a broad spectrum of mycotoxins has facilitated the screening of a larger number of samples for contamination with a wide array of less well-known “emerging” mycotoxins and other metabolites. In this study, 83 samples of feed and feed raw materials were analysed. All of them were found to contain seven to 69 metabolites. The total number of detected metabolites amounts to 139. Fusarium mycotoxins were most common, but a number of Alternaria toxins also occurred very often. Furthermore, two so-called masked mycotoxins (i.e., mycotoxin conjugates), namely deoxynivalenol-3-glucoside (75% positives) and zearalenone-4-sulfate (49% positives), were frequently detected. Although the observed median concentrations of the individual analytes were generally in the low μg/kg range, evaluating the toxicological potential of a given sample is difficult. Toxicity data on less well-known mycotoxins and other detected metabolites are notoriously scarce, as an overview on the available information on the most commonly detected metabolites shows. Besides, the possible synergistic effects of co-occurring substances have to be considered.
Mycotoxins are a chemically diverse group of toxic secondary fungal metabolites that can occur in a wide array of commodities. Strictly speaking, they are defined as secondary metabolites of fungal origin exhibiting in vivo toxicity towards vertebrates after introduction via a natural route (i.e., ingestion, inhalation etc.) . Contamination results from fungal infection and proliferation in the field or during storage [2,3]. Legal authorities, food and feed industry alike acknowledge the importance of this issue and considerable effort is directed towards detecting and preventing mycotoxin contamination. However, of the 300–400 mycotoxins known to date , only a very limited number is subject to legal guidance and regular monitoring. Regarding feed, aflatoxins (AF), fumonisins (FB), deoxynivalenol (DON), zearalenone (ZEN) and ochratoxin A (OTA) are most often tested for . Still, many analytical methods used for the determination of fungal metabolites are specific for one mycotoxin or a closely related group of mycotoxins. Therefore, a separate analysis is required for each mycotoxin of interest, an important constraint for monitoring a large number of mycotoxins. The development of multi-mycotoxin LC-MS/MS methods was a major step towards overcoming this problem. A very powerful method was established by Sulyok et al. in 2006  and has been continuously extended ever since [6,7]. The parameters for the detection of 186 metabolites have been published by Vishwanath et al. , and the same group has expanded the method to cover 320 fungal, bacterial and plant metabolites since then.
In addition to providing information on occurrence and concentration levels of an increasing number of usually neglected mycotoxins multi-mycotoxin LC-MS/MS methods also help to address the issue of masked mycotoxins. Masked mycotoxins are mycotoxin conjugates that typically remain undetected when testing for the parent toxin. They may be formed as part of the plant’s defence mechanism (e.g., DON-3-glucoside or ZEN-4-glucoside), and in some cases, e.g., hidden fumonisins, masked mycotoxins even develop during food processing . Apart from exerting toxic effects of their own there is evidence suggesting that some masked mycotoxins are reconverted into the parent toxin during digestion, further adding to the toxicity of the respective food or feed [10,11,12,13].
Ever since 2005, BIOMIN has conducted a survey program monitoring the worldwide prevalence and concentration of aflatoxins, fumonisins, deoxynivalenol, zearalenone and ochratoxin A in feed and feed raw materials [14,15,16,17,18,19,20]. Additionally, in an effort to further broaden the knowledge on mycotoxin occurrence and co-occurrence in feed, 83 samples were subjected to multi-mycotoxin LC-MS/MS analysis. The results are presented in this paper, including an overview of the currently available toxicity data for the most commonly detected “novel” or “emerging” mycotoxins (i.e., mycotoxins that have not received as much scientific attention as AF, FB, DON, ZEN and OTA).
A total number of 139 different fungal metabolites were detected in the 83 feed samples (Table 1). All of the samples were co-contaminated with seven to 69 different mycotoxins (Figure 1). The co-occurrence of 28 metabolites was most frequent, observed in n = 9 of the samples. Figure 2 shows the distribution of the detected concentrations for metabolites that were detected in more than 60% of the samples.
|Mycotoxin/metabolite||n (pos)||% pos||Median (μg/kg)||Max (μg/kg)||Mycotoxin/metabolite||n (pos)||% pos||Median (μg/kg)||Max (μg/kg)|
|sum of Enniatins||80||96||30||5441||Tetracycline (ab)||5||6||77||10,696|
|Enniatin A1||79||95||5.5||2216||Versicolorin C **||5||6||0.8||89|
|Enniatin B||76||92||11||780||Amoxycillin * (ab)||4||5||NA||NA|
|Enniatin B1||76||92||14||2690||Andrastin D *||4||5||NA||NA|
|Alternariol methyl ether||68||82||1.4||733||Secalonic acid D||4||5||4.5||369|
|Avenacin Y||26||31||209||9948||Paspalitrem A *||3||4||NA||NA|
|Macrosporin A||26||31||3.3||9.1||Rubellin D||3||4||259||1188|
|Monocerin||24||29||0.9||2644||sum of Aflatoxins||2||2||0.24 a||861|
|Siccanol *||23||28||9607||39850||Aflatoxin B1||2||2||0.24 a||699|
|3-Nitropropionic acid||19||23||6||392||Aflatoxin B2||1||1||-||63|
|sum of Fumonisins||18||22||203||57,667||Aflatoxin G1||1||1||-||69|
|Fumonisin B1||18||22||142||40,300||Aflatoxin G2||1||1||-||4.4|
|Fumonisin B2||18||22||38||10,372||Aflatoxin M1||1||1||-||26|
|Fumonisin B3||14||17||18||3859||Cyclopiazonic acid||2||2||37 a||2319|
|Fumonisin B4||7||8||112||3136||Diacetoxyscirpenol||2||2||0.04 a||2.7|
|Fusaric acid||18||22||643||13,593||Ergocornine||2||2||19 a||25|
|HT-2 Toxin||18||22||13||1910||Ergocristam *||2||2||17,370 a||19230|
|Chrysophanol||17||20||8.2||41||Ergocristinam *||2||2||7181 a||8233|
|Mycophenolic acid||17||20||40||21,856||Ergovalin||2||2||1 a||5.4|
|Averufin **||16||19||0.4||215||Gibberellic acid||2||2||9.7 a||89|
|Bikaverin *||14||17||27510||51,130||Neosolaniol||2||2||0.7 a||290|
|Fusaproliferin||14||17||2555||14,844||Penicillic acid||2||2||12 a||13|
|Fusarinolic acid **||13||16||643||13,965||Radicicol||2||2||5.3 a||5.9|
|Kojic acid||10||12||75||3172||Calphostin C||1||1||-||431|
|Andrastin A *||7||8||4814||7603||Cycloaspeptide A||1||1||-||4.6|
|Paspalin *||6||7||NA||NA||Malformin A **||1||1||-||8|
|Ergometrin||5||6||6.8||26||Norsolorinic acid **||1||1||-||1.6|
|Paxillin||5||6||5017||94,860||Versicolorin A **||1||1||-||27|
a minimum in µg/kg; * no standard available for quantification (if a standard became available at some point, the results samples analysed thereafter are shown in the median/maximum column); ** semi-quantified using response factor of a structurally related analyte; ab: antibiotic, plt: plant metabolite, NA: not applicable.
Beauvericin (BEA) was found most often. It was detected in 98% of the samples. Enniatins (ENN) were second most common, with 96% of the samples testing positive followed by DON and emodin with 89% positives each.
The samples listed in Table 1 include six maize cob samples from Lower Austria that all had visible signs of mould infection, ranging from slightly infected (n = 4) to severely moulded (n = 2). Two of those samples were obtained in 2010 and the other four in 2012. All samples were acquired directly after harvest. The results per sample are specified in Table 2.
|Mycotoxin/metabolite||Samples, concentrations in μg/kg|
|2010-1 *||2010-2||2012-1||2012-2||2012-3||2012-4 *|
* Heavily moulded.
The six maize cob samples were co-contaminated with 15 to 25 metabolites, which are below the average of 28 co-occurring metabolites observed in the pool of samples as a whole. Great differences were observed regarding the mycotoxin concentrations and contamination pattern depending on the year of analysis. Mono- and di-acetoxyscirpenol for example were only detected in the 2010 samples, while tentoxin and tenuazonic acid were only detected in 2012 (bikaverin, fusaric acid, fusarinolic acid and siccanol were not covered by the 2010 method). Nivalenol levels were higher in 2010, while fusaproliferin concentrations were more elevated in 2012 (sample 2010-2 had the highest nivalenol concentration, and sample 2012-1 had the highest fusaproliferin concentration of all 83 samples). It is interesting to note that the mycotoxin levels and contamination pattern were quite different for samples sourced in the same year as well in some cases. The enniatin concentrations in the heavily moulded cob from 2010 (2010-1) were many times higher than those detected in the other samples. This sample also contained higher levels of fusaproliferin or moniliformin than the other 2010 sample, but had much lower levels of aurofusarin, mono- and di-acetoxyscirpenol or nivalenol. Sample 2012-4 (severe mould infection), for example, contained much higher levels of aurofusarin, DON and DON-3-glucoside than any of the other samples and was the only sample contaminated with 3-acetyl-DON, 15-acetyl-DON, 15-hydroxyculmorin, α-zearalenol, β-zearalenol, culmorin, ZEN or ZEN-4-sulfate. In fact, the observed concentrations of DON, ZEN, aurofusarin, DON-3-glucoside, ZEN-4-sulfate and 3-acetyl-DON in this sample were the highest in the entire study. On the other hand, it did not contain fusaproliferin, which was present at rather high concentrations in the other three samples from 2012. These results suggest that the fungal populations on a given year’s cobs were different, despite the fact that the cobs were obtained from the same field.
Furthermore, the pool of samples includes three US maize samples that were selected for LC-MS/MS analysis after “conventional” high-performance liquid chromatography (HPLC) analysis showed a high contamination with DON (n = 2) or fumonisins and aflatoxins (n = 1). This was done in order to identify co-occurring metabolites in samples with excessively high concentrations of regulated mycotoxins. Both samples with high DON levels (17,360 and 15,684 μg/kg) also had high levels of DON-3-glucoside (2696 and 1977 µg/kg), aurofusarin (4155 and 12,908 µg/kg), ZEN (1137 and 378 μg/kg) and ZEN-4-sulfate (61 and 26 μg/kg). Fumonisin levels were low in both samples (sum of fumonisins: 35 and 56 μg/kg). The latter sample also had the highest concentration of 15-hydroxyculmorin detected in this study. The samples were co-contaminated with 11 and 45 metabolites, respectively. The aflatoxin and fumonisin contaminated sample tested positive for 69 metabolites. Apart from containing the highest aflatoxin and fumonisin levels observed in this study, it also had the highest level of cyclopiazonic acid, moniliformin and fusarinolic acid. Furthermore, 49 μg/kg alternariol, 39 μg/kg alternariol methyl ether and 30 μg/kg OTA were detected amongst others. DON and ZEN concentrations were low in this sample (79 and 3 μg/kg, respectively).
The results of the analysis of 83 samples with a multi-mycotoxin method based on LC-MS/MS clearly show that mycotoxin co-contamination is the rule. Mixtures of Fusarium toxins are detected most frequently, which is in line with the findings of two other studies using the same LC-MS/MS method on African food and feed samples [21,22]. Given the fact that Fusarium species are plant pathogens of major importance worldwide, particularly in cereal production, this is not surprising. Their occurrence in cereals and feed on a global scale was reviewed by Placinta et al. . Bottalico  published an extensive review on the occurrence of various Fusarium spp. in Europe, including their mycotoxin profiles. Most species were reported to simultaneously produce a number of mycotoxins. Additionally, crops are almost always infected by several different fungal species at once. Bottalico  stated that it was quite common to isolate up to nine different Fusarium spp. from a single piece of infected tissue. Taken together, these facts explain the high prevalence of Fusarium mycotoxins in the analysed samples.
Except for specifically selected high contamination samples, the concentrations of individual mycotoxins were generally low and almost always well below the respective EC maximum level or guidance value (maximum levels exist for aflatoxin B1 (AFB1) , guidance values exist for DON, ZEN, FB1 + FB2 and OTA ) in feed. As for DON, the frequent detection of DON-3-glucoside (DON-3-Glc) should be mentioned. It always co-occurred with DON and was detected in 75% of the samples. Given that several lactic acid bacteria commonly found in the digestive tract of mammals were recently reported capable of cleaving a significant proportion of DON-3-Glc, releasing DON , the presence of DON-3-Glc is likely to increase the total bio available amount of DON in contaminated feed. In this study, DON-3-Glc was detected at concentrations attaining on average 12% of the DON contamination level of the respective sample. This percentage is in line with the findings of De Boevre et al. , who reported that DON-3-Glc accounted for up to 14% of the average total DON equivalents detected in feed samples. Nevertheless, even supposing the unlikely event of a 100% conversion of DON-3-Glc to DON during digestion and disregarding specifically selected high contamination samples, only two wheat samples came close to surpassing the respective European Commission (EC) guidance value. Recent results obtained from rat studies suggest, however, that the bioavailability of DON-3-Glc is low . ZEN-4-sulfate (ZEN-4-S), a masked form of ZEN, was also detected frequently. This mycotoxin conjugate is readily hydrolysed in acidic conditions . Hence, ZEN is released during digestion of ZEN-4-S contaminated diets.
Concerning the mycotoxins other than DON and ZEN listed in Table 1, data on toxicity, especially in vivo data, are scarce. Available data are summarised in Table 3. BEA and ENN exhibit low acute toxicity in vivo . It is, however, unclear to what extent they influence the toxic effects of other mycotoxins. BEA in particular was reported to be a chemo sensitising agent with the potential to increase the efficacy of antibiotics, as well as chemotherapeutic anti-cancer drugs .
Emodin has also been investigated for its pharmacologic properties. It is a major chemical constituent of Chinese rhubarb (Rheum palmatum) roots and has been reported to exert anti-inflammatory, anti-arteriosclerotic and immunosuppressive effects. Furthermore, it inhibits the proliferation of various cancer cell lines , increases the effect of gemcitabine on pancreatic cancer in mice  and has been proposed as possible treatment for type-2 diabetes .
|Alternariol||Alternaria sp. |
|conflicting results regarding mutagenic activity (strongly mutagenic in Bacillus subtilis rec assay and E. coli ND 160 reverse mutation assay; weak to no mutagenic activity in Ames test) |
genotoxic (causes DNA strand breaks by interacting with mammalian topoisomerases); implicated as risk factor for oesophageal cancer (reviewed in )
no mortality or teratogenic effects in chicken embryos at doses up to 1000 mg/egg 
|Alternariol methyl ether||Alternaria alternata, |
|genotoxic (causes DNA strand breaks by interacting with mammalian topoisomerase IIα) (reviewed in ); brain haemorrhages and bleeding in cerebral ventricles; effect on progesterone synthesis in pigs; therefore, postulated effect on reproductive performance in pig and other mammalian species  |
precancerous changes in oesophageal mucosa of mice fed 100 mg/kg bw/day for 10 months, also causing weight loss, lower food consumption (less toxic effect than tenuazonic acid (25 mg/kg bw/day for 10 months)) 
no mortality or teratogenic effects in chicken embryos at doses up to 500 mg/egg; 
|Apicidin||Fusarium sp. |
F. pallidoreseum (F. semitectum)
|histone deacetylase inhibitor, broad spectrum antiprotozoal activity ; antiproliferative  and apoptotic  in various cancer cell lines |
brine shrimp larvae:
LD50: 40 mg/mL; 
died with 0.05% apicidin supplementation of diet; apicidin causes body weight loss, haemorrhage in the stomach, intestines and bladder 
|major effect on poultry are changes in egg yolk colour from yellow-orange to dark-brown [41,42]; |
decrease of protein and fat content in chicken meat 
26.4 mg/kg feed influenced quality of eggs—decrease in vitamins E, A, total carotenoid, lutein and zeaxanthin concentrations and significantly increased egg yolk susceptibility to lipid peroxidation 
26.4 mg/kg feed compromised the immune system of the progeny 
F. poae [46,47]
|antibacterial, insecticidal, cytotoxic, (reviewed in [29,48]); ionophoric properties cause dysfunction of mitochondria  and induces apoptosis (reviewed in [29,48]); co-occurs with enniatin A ; bioactivities are different to enniatins due to 3 N-methylphenylalanyl residues  |
acute toxicity (summarised in )
mice: LD50: ≥10 mg/kg bw, intraperitoneal; ≥100 mg/kg bw oral
low/no acute toxicity in:
duckling (100 mg/kg bw, gastric intubation)
turkey (2.5 mg/kg feed)
broiler (12 mg/kg feed)
|Brevianamide F||Penicillium brevicompactum|
precursor of the fumitremorgins and the tryprostatins [51,52]
also produced by Streptomyces sp. 
|myocardial oxidative damage;  oxidative injuries in chick embryonic livers and kidneys ; growth retardation and differentiation inhibition in vitro in rat embryos ; probably implicated in fescue foot disease ; anti-marine-fouling compound—toxic to zebra fish embryos by inducing apoptosis  |
mice: LD50: 44 mg/kg bw, intraperitoneal; 275 mg/kg bw oral 
died after 68 and 39 mg/kg for 2 and 3 days oral dosage; with smaller dosage, development of petechial haemorrhages and acute inflammation of gastric compartments ( in )
|Culmorin||F. culmorum, |
|low toxicity in several in vitro assays, Ames test negative , co-occurrence with DON  |
some minor non-significant effects on growth and feed consumption (2 mg/kg feed) with and without DON (6 mg/kg feed) 
|15-Hydroxy-culmorin||F. graminearum |
|co-occurrence with culmorin and DON  |
no evidence of acute toxicity to mammals so far 
|possibly genotoxic ; cytotoxic, antitumour, antibacterial, anti-inflammatory, immunosuppressive  |
active ingredient of various Chinese herbs, potential drug for therapy of type-2 diabetes 
induces embryonic toxicity in mouse blastocysts through apoptosis; 
LD50: 3.7 mg/kg bw 
clinical symptoms in cockerels included loss of appetite, accumulation of faecal material with acute epidermal irritation around the cloaca, general debilitation and mortality within 5 days of ingestion;
0.25 μg/mL negatively affected embryo survival and hatching success; toxic to larvae at relatively low concentrations 
|antibacterial, antifungal, herbicidal, insecticidal, ionophore, induction of apoptosis [29,49,69,70] |
enniatin B often occurs together with enniatin B1 and enniatin A with beauvericin 
mice: 10–40 mg/kg bw, intraperitoneal, every 8 h: mice died within 2–5 days;
doses <10 mg/kg bw resulted in reduced body weight 
brine shrimp: 50 μg enniatin B/mL killed almost all after 24 h;
ranking in brine shrimps: enniatin B > B1 > A1 > A, mixture of all four most toxic 
|antibiotic activity against Gram-positive bacteria ; potent inhibitor of HIV-1 integrase enzyme  |
mice: LD50: 63.0 mg/kg bw, intraperitoneal 
|1-day-old chicks: LD50: 5.4 mg/kg bw oral  |
7-weeks-old broilers: LD50: 1.38 mg/kg bw, intravenous 
broilers: 50 mg/kg feed toxic for broilers fed to market age, resulting in lower body weight gain, less efficient feed converting rate, higher mortality ; additive effects with aflatoxin , as well as with deoxynivalenol 
turkeys: 37.5 mg/kg feed hepatotoxic; 25 mg/kg feed cardiotoxic 
swine:100 mg/kg feed for 28 days in growing barrows reduced body weight, body weight gain and feed consumption and affected serum biochemical analytes; 50 mg/kg feed influence on haematologic values ; additive effects with fumonisin B1
sheep: 10 mg/kg bw, intubation caused death after 18 h, also degeneration of the proximal tubules of kidneys 
|Tentoxin||Alternaria alternata||induces chlorosis in germinating seedlings of many dicotyledonous plants |
|Tenuazonic acid||Alternaria sp. |
LD50: 81 mg/kg bw oral, female; 186 mg/kg bw oral, male ;
risk for oesophageal cancer: toxic effect on oesophageal mucosa of mice (25 mg/kg bw/day oral for 10 months) stronger than with alternariol methyl ether (100 mg/kg bw/day oral for 10 months)—resulting in weight loss and lower feed consumption 
rats: LD50: 168 mg/kg bw oral, female; 180 mg/kg bw oral, male 
young chicken: LD50: 37.5 mg/kg bw oral 
1.25–1.50 mg/kg bw/day (3-weeks oral) induced microscopic and macroscopic lesions in various tissues and significant weight loss 
|in vitro: |
cytotoxic, cytostatic, genotoxic effects in lymphocytes ; 2 mM (24h) damages DNA in HepG2, A549 and THP-1 cells (comet-assay) ; induction of apoptosis in leukaemic blood monocytes cell line U937 
mice: LD50: 351 mg/kg bw, intraperitoneal 
As for the Alternaria metabolites alternariol, alternariol methyl ether, tenuazonic acid and tentoxin, only the first three are of toxicological concern. Tentoxin exhibits herbicidal properties [64,89], as it induces chlorosis by inhibiting chloroplast development . It does not even figure in some reviews on Alternaria mycotoxins (e.g., Scott ) or is mentioned in passing as co-occurring with more important toxins, such as alternariol or alternariol methyl ether [33,91]. Alternariol and alternariol methyl ether have received some attention, due to their mutagenic and genotoxic properties. Their acute toxicity is rather low [33,90,91]. Tenuazonic acid is considered the most acutely toxic of the Alternaria mycotoxins . Exposure to sub-lethal levels of tenuazonic acid (10 mg/kg) negatively affects feed efficiency in chicken and causes lesions on various organs . The occurrence of Alternaria mycotoxins in food and feed in general was not deemed a significant health hazard in a report submitted to the European Food Safety Authority (EFSA), owing to the low naturally occurring contamination levels . The EFSA panel on contaminants in the food chain (CONTAM) stated that a risk assessment for Alternaria mycotoxins in feed was not possible, due to a lack of information on occurrence and toxicity .
Data on culmorin and its hydroxylated analogues do not indicate acute toxicity to mammals . Moniliformin (MON) in vivo toxicity has been investigated more extensively. Poultry seem to be the most sensitive species. The main acute symptoms are muscular weakness, respiratory stress and myocardial degeneration , and chronic exposure will result in reduced weight gain, impaired immune system and myocardial lesions . Following a study on 270 male broiler chicks, Ledoux et al.  concluded that feed containing >50 mg/kg MON will exert toxic effects on these animals. The concentrations observed in this study are well below this limit. In fact, occurrence data summarised in the report submitted to EFSA suggest that naturally contaminated samples do not normally exhibit contamination at such a high level. Studies reporting MON concentrations near or exceeding this proposed tolerance level usually refer to contamination in handpicked, visibly Fusarium-damaged samples .
4. Experimental Section
From 2010 on, a total number of 83 naturally contaminated samples of feed and feed raw materials were analysed with a semi-quantitative multi-mycotoxin LC-MS/MS method. The majority of the samples were feed samples (n = 35). Besides, samples of silage (n = 21), maize (n = 15), wheat and wheat by-products (n = 6), barley straw (n = 3) and other feed ingredients (soybeans, sunflower seeds etc., n = 3) were tested. The majority of the samples were sourced in Europe (n = 71), most often originating from Hungary (n = 19), Austria (n = 17) and Denmark (n = 15). Other European samples were obtained in Belgium, Italy, Norway, Russia, the UK and Ukraine. The remainder of the samples was sourced in America (n = 8, from Brazil, Canada and the USA) and Australia (n = 4). The pool of samples comprised a small number of samples (n = 9) that were known or expected to contain high levels of mycotoxins. These were three samples of US maize that had been found to contain high levels of DON (n = 2) or AF and FB (n = 1) using “conventional” HPLC analysis and six samples of maize cobs displaying different degrees of visible mould infection. The maize cob samples were all taken from the same field in Lower Austria in the 2010 (n = 2) and 2012 (n = 4) growing season.
The analyses were conducted at IFA-Tulln. All samples were analysed for the presence and concentrations of fungal metabolites by LC-MS/MS according to Vishwanath et al. . The analytical method has been extended to cover 320 metabolites, transferred to a more sensitive mass spectrometer and pre-validated for four matrices . In brief, 5 g of sample was weighed into a 50 mL polypropylene tube (Sarstedt, Nürnbrecht, Germany) and extracted with 20 mL acetonitrile/water/acetic acid (79:20:1, v/v/v) for 90 min on a GFL 3017 rotary shaker (GFL, Burgwedel, Germany). Extracts were diluted in extraction solvent (ratio 1:1) and directly injected into the LC-MS/MS instrument.
Chromatographic separation was performed at 25 °C on a Gemini® C18-column, 150 × 4.6 mm i.d., 5 μm particle size, equipped with a C18 4 × 3 mm i.d. security guard cartridge (all from Phenomenex, Torrence, CA, USA) and coupled to an 1290 Series HPLC System (Agilent, Waldbronn, Germany). Chromatographic separation was performed at 25 °C on a Gemini® C18 column (Phenomenex, Torrance, CA, USA). After an initial time of 2 min at 100% eluent A, the proportion of eluent B was increased linearly to 50% within 2–5 min and 100% within 5–14 min, followed by a holding-time of 4 min at 100% eluent B and 2.5 min column re-equilibration at 100% eluent A pumped at a flow rate of 1 mL/min.
A QTrap 5500 LC-MS/MS System (Applied Biosystems, Foster City, CA, USA) equipped with a TurboIonSpray electrospray ionization (ESI) source was used to detect and quantify the fungal metabolites. ESI-MS/MS was performed in the scheduled multiple reaction monitoring (sMRM) mode, both in positive and negative polarities in two separate chromatographic runs per sample by scanning two fragmentation reactions per analyte with the following settings: source temperature 550 °C; curtain gas 30 psi; ion source gas 1 (sheath gas) 80 psi, ion source gas 2 (drying gas) 80 psi, ion spray voltage −4500 V and +5500 V, respectively, collision gas (nitrogen) medium. The MRM detection windows were 54 and 96 s in the positive and negative ionization mode, respectively, and the cycle time was set to one second.
Mycotoxins were quantified by external calibration (1/x weighted) using a multi-component standard prepared from authentic standards.
Multi-mycotoxin LC-MS/MS analysis is a valuable tool for obtaining a more accurate picture of mycotoxin contamination pattern in feed and feed raw materials. Key advantages of such methods are the detection of masked mycotoxins and the detection of mycotoxins that are usually not tested for.
Mycotoxin conjugates can make up a significant proportion of the total mycotoxin contamination, particularly regarding DON and ZEN . In view of the possible reconversion of some mycotoxin conjugates (e.g., DON-3-Glc and ZEN-4-sulfate) to the parent toxin during digestion the occurrence of high proportions of masked mycotoxins might add significantly to the toxicity of the feed. Yet, little is known about the extent of masked mycotoxin reconversion during digestion (recent results suggest low bioavailability in rats ), and more research is needed in this field.
The total number of detected metabolites amounts to 139, which is about twice as high as in previous studies applying the same method to African food and feed samples [21,22]. Yet, evaluating the risk associated with the presence of a given analyte proves difficult for the vast majority of the metabolites. Table 3 highlights the lack of toxicity data on these substances and the need for further research in this area. As exposure to acutely toxic concentrations is less common than chronic exposure to low levels of a metabolite, potential adverse effects of long-term low-level exposure should be the focus of future research efforts.
The co-occurrence of seven to 69 metabolites per sample further complicates the evaluation of the feed material’s toxicological potential. Additive and synergistic effects on overall toxicity are frequently observed when mycotoxin mixtures are evaluated instead of single toxins. This is particularly true at sub-acute concentrations considering that most studies investigating the effect of mycotoxin combinations on animal performance at these levels found additive or synergistic effects . In addition, naturally DON contaminated feed frequently proved more toxic than artificially contaminated feed containing the same concentration of the toxin [98,99]. This testifies to the fact that interactions of co-occurring metabolites can enhance the overall toxic effect of single mycotoxins. Consequently, data on the interactions of “novel” mycotoxins and other metabolites with each other and with regulated mycotoxins (AF, FB, DON, ZEN and OTA) are needed.
In conclusion, multi-mycotoxin LC-MS/MS analysis is an important step towards gaining a more accurate picture of the extent of mycotoxin contamination in agricultural commodities, food and feed. However, highlighting the frequent occurrence of both masked and usually neglected “emerging” mycotoxins, the results of such analyses also emphasise the fact that considerable research effort is still required in this field. In order to permit an accurate assessment of the risks associated with the presence of these contaminants more data is needed on their metabolic fate (particularly concerning masked mycotoxins), their toxicities and possible synergistic interactions with other mycotoxins present.
Conflict of Interest
The authors declare no conflict of interest.
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