1. Introduction
Cereal-based food crops are an important part of the culinary heritage of multiple cultures all over the world. In the Northern African region, food intakes are based mainly on cereals such as wheat, barley, maize, and sorghum consumed as raw grains, flours, or processed products. Furthermore, cereals are susceptible to fungal diseases such as Fusarium Head Blight (FHB) caused by Fusarium species. The disease reduces the yield of harvested cereals and impacts the quality of grains, which become starchy and inadequate for industrial processing.
The different
Fusarium species causing this disease are mainly
F. graminearum,
F. culmorum,
F. pseudograminearum,
F. avenaceum,
F. equiseti, and
F. poe. These
Fusarium species are able to produce mycotoxins defined as toxic secondary metabolites of low molecular weight, are thermally stable and have a high bioaccumulation ability in crops from sowing to harvesting in the field, but also at storage and during food processing [
1]. Mycotoxins at high concentrations are potentially harmful to humans’ and animals’ health. The most known
Fusarium mycotoxins in cereals are Type B Trichothecene (TCTB) including deoxynivalenol (DON) and its acetylated derivatives, Type A Trichothecenes, Fumonisins, and Zearalenone (ZEA). They have a wide range of harmful effects such as carcinogenicity, teratogenicity, and mutagenicity [
2]. A less known
Fusarium mycotoxins group, called “emergent mycotoxins”, is receiving increasing interest from researchers. Enniatins (ENNs), Beauvericin, and Moniliformin mainly make up this group [
3]. Although no acute toxicity was reported from the exposure to these mycotoxins, in vitro studies demonstrated their cytotoxicity on different cell lines, their ability to impair cell cycle distribution, to cause mitochondrial dysfunction, and to induce apoptosis. Moreover, their presence in large amounts and their natural co-presence with other mycotoxins may induce synergistic effects [
4]. Among the 29 identified ENNs, four analogs are the most detected in cereal grains, enniatin A (ENA), enniatin A1 (ENA1), enniatin B (ENB), and enniatin B1 (ENB1) [
4]. Most of the
Fusarium strains that have been reported to produce these ENNs in cereals are part of the
F. sambucinum species complex (i.e.,
F. venenatum and
F. poae) as well as the
F. tricinctum species complex composed by
F. tricinctum,
F. avenaceum,
F. torulosum, and
F. acuminatum [
5].
Several
Fusarium species have been found in cereals cultivated or consumed in Tunisia. Studying FHB symptomatic heads at the filling stage from 11 wheat fields in Northern Tunisia during the 2004 and 2007 crop seasons, these were found as the main
Fusarium species:
F. culmorum,
F. avenaceum, and
F. equiseti [
6]. In another study during the 2004 crop season on infested durum wheat spikes, it was reported that the most common species isolated were
Microdochium nivale var
nivale (63.5%),
F. culmorum (26%),
F. pseudograminearum (9%), and
F. avenaceum (1.5%) [
7]. When determining the mycoflora of wheat and barley grain samples consumed in Tunisia in 2011, Jedidi et al. [
8] isolated
Fusarium species from 18% of wheat and 50% of barley samples, with a mean percentage of infected grains per sample of 1.17% and 1.1% in wheat and barley grains, respectively. The main
Fusarium species they isolated was
F. equiseti. To the best of our knowledge, no report has been conducted about the isolation of
F. acuminatum from cereals produced in Tunisia. It is obvious that the prevalent
Fusarium species found in Tunisian wheat grains are producers of TCTB or ENNs. However, in a multi-mycotoxin analysis in 34 wheat and 5 barley samples of asymptomatic grains from Tunisian markets in 2009, Oueslati et al. [
9] did not detect TCTB. In another study focused on the detection of emerging mycotoxins, it was shown that 96% of the analyzed wheat and barley samples were contaminated with different ENNs [
10].
Key global actions for mycotoxin management in wheat and other small grains have recently been reviewed [
11]. The use of fungicides is one of them. The efficiency depends on the active molecule, the application timing, method and rate, the cereal variety, and the populations and species of
Fusarium present [
11]. However, to limit the accumulation of pesticide residues in the environment and in food, and the dependency on the companies producing them, alternatives to synthetic fungicides using local resources are actively searched for in various countries. The use of non-toxic and eco-friendly plant essential oils (EOs) is one alternative. Some EOs have been shown to be effective against
Fusarium species and their production of mycotoxins [
12,
13,
14,
15]. Finding alternatives to synthetic fungicides for controlling local populations of
Fusarium spp. causing mycotoxin contamination of wheat and small grain cereals is of concern in Tunisia and other Mediterranean countries, as a contribution to the improvement in food safety.
The present work aimed at improving the knowledge on the contamination of non-symptomatic Tunisian wheat grains by Fusarium species and mycotoxins (both regulated and emerging groups), and to shed light on F. acuminatum, a rarely found species that had never been associated with ENNs production in Tunisian cereals before. A strain isolated from the studied Tunisian wheat grains was characterized as a potential source of ENNs contamination. Its susceptibility to EOs from eight Tunisian plants was assessed.
2. Materials and Methods
2.1. Wheat Samples
Twenty-three samples of wheat grain from various varieties were randomly collected at harvest time at the locality of Béjà (North West Tunisia), representing six durum wheat varieties (Karim, Khiar, Maâli, Nasr, Om Rabii, Razzek) and four bread wheat varieties (Byrsa, Hidra, Salambôo, Utique) on two years, 2017 and 2018, and three additional bread wheat varieties (Vaga, Tahent, Badii) in 2017. All the samples were stored in hermetic polyethylene bags at room temperature until mycotoxins analysis and isolation of Fusarium species.
2.2. Mycotoxin Extraction from Wheat Grains
Mycotoxin extraction from grains was adapted from a previously published method [
16]. The homogenized grains were dried at 50 °C for 48 h, then ground into a fine powder (particles size <100 µm). Five g of powder were extracted with 20 mL acetonitrile/water (84:16,
v/v) rotating end-over-end at 50 rpm for 60 min, followed by centrifugation (4 °C, 10 min at 3000×
g) and the supernatant was collected. The fraction was either directly evaporated to dryness under a gentle nitrogen stream for further analysis of ENNs or purified through a trichothecene P
® column (R-Biopharm, Darmstadt, Germany) and 4 mL of the eluate was collected before drying by evaporation for further analysis of TCTBs and ZEA.
2.3. Mycotoxin Analysis—TCTB and ZEA
The dried extracts were resuspended in methanol/water (1:1, v/v) and filtered through a 0.2 µm filter (Phenomenex, Le Peck, France) for the quantification of ZEA and TCTBs, including DON and its 15 and 3 acetylated derivatives (3-ADON and 15-ADON), Nivalenone (NIV), and its derivative, Fusarenon X (FUS-X), using an Agilent Technologies 1100 series HPLC chain, equipped with an Agilent photodiode array detector (DAD) and the ChemStation chromatography manager software (Agilent, Waldbronn, Germany). The injection volume was 10 µL. Separation was achieved on a Kinetex XB-C18 100 Å column (150 × 4.6 mm2, 2.6 μm) (Phenomenex, Le Peck, France) maintained at 45 °C. The mobile phase consisted of acidified water with ortho-phosphoric acid, pH 2.6 (solvent A), and acetonitrile (solvent B), and the following elution gradient was used: starting at 93% A and 7% B for 1 min, 93% to 70% A and 7 to 30% B in 10 min, 70 to 10% A and 30 to 90% B in 10 min, 10 to 93% A and 90 to 7% B in 2 min, and 5 min post-run equilibration with the initial conditions. The flow rate was kept at 1 mL min−1 for a total run time of 27 min. UV-VIS spectra were recorded from 220 to 550 nm and peak areas were measured at 230 nm. Quantification was performed using external calibration ranging from 6.25 to 100 µg mL−1 prepared with standard solutions (Romer Labs, Tulln, Austria). The limit of quantification was 0.1 µg g−1 grain for each of the mycotoxins.
2.4. Mycotoxin Analysis—ENNs
For the quantification of ENNs, the dried extracts were resuspended in acetonitrile/water (85:15, v/v), vortexed, filtered through 0.45 µm filters, and 10 µL was injected in an Agilent Technologies 1100 series HPLC chain, equipped with an Agilent photodiode array detector (DAD) (Agilent, Waldbronn, Germany) for separation on a Zorbax Eclipse XDB-C8 (4.6 × 15 mm2, 5 µm) maintained at 30 °C. The mobile phase consisted of MilliQ water (solvent A) and acetonitrile (solvent B). The flow was kept at 1 mL min−1 for a total run time of 26 min. The elution gradient was: 30% A and 70% B for 5 min, 30 to 10% A and 70 to 90% B in 10 min, 10% A and 90% B for 5 min, 10 to 30% A and 90 to 70 % B in 1 min, 30% A and 70% B for 5 min. Absorbance spectra were recorded from 190 to 450 nm and peak areas were measured at 205 nm. Quantification was performed using external calibration ranging from 1 to 100 µg mL−1 prepared with standard solutions of enniatin A (ENA), enniatin A1 (ENA1), enniatin B (ENB), enniatin B1 (ENB1) (Sigma-Aldrich, Saint-Quentin-Fallavier France). The limit of detection was 0.01 µg g−1 of grain.
Alternatively, to check the presence/absence of the targeted mycotoxins measured with the HPLC/DAD method, five samples collected in 2018 were randomly selected for extractions and LC-MS/MS analysis performed as in Ducos et al. [
16] using a QTrap 2000 system (AB Sciex, Courtaboeuf, France) equipped with an Electro Spray Ionization (ESI) source and an 1100 Series HPLC system (Agilent, Les Ulis, France), as an alternative to the HPLC-DAD analysis presented above. Calibration in the matrix was performed using pure standards of ENA, ENA1, ENB, ENB1 (Sigma-Aldrich, France) diluted at 10 to 250 ng mL
−1. Retention times were 6.35, 6.28, 6.11, 6.20 min for ENA, ENA1, ENB, ENB1, respectively, and their precursor ions were 699.49, 685.48, 5657.44, and 671.46 m/z, respectively. The limit of detection was 0.8 ng g
−1 of grain
2.5. Fusarium Selection, Isolation and Microscopic Characterization
The sample’s contamination with
Fusarium species was after surface sterilization. A total of 100 grains alternatively selected from each sample were soaked in 10% sodium hypochlorite for 5 min and rinsed 3 times with sterile deionized water before being placed on potato dextrose agar (PDA) medium. After incubation for 3 to 5 days at 25 °C, the mycelial growth was examined and plugs from the different mycelial colonies were transferred to new PDA plates. Monosporic cultures were obtained by suspension dilutions followed by isolation under a stereomicroscope of one germinated spore per isolate. The monosporic cultures were morphologically identified according to Leslie and Summerell keys [
17]. The macroscopic examination of the cultures of the fungal species was carried out on PDA and on FDM-agar medium the composition of which was: 12.5 g of glucose, 4.25 g of NaNO
3, 5 g of NaCl, 2.5 g of MgSO
4·7H
2O, 1.36 g of KH
2PO
4, 0.01 g of FeSO
4·7H
2O, 0.0029 g of ZnSO
4·7H
2O, 15 g of agar, 1 L of water [
18]. The characteristics of micro- and macroconidia (appearance of the conidiophore, form, and size) were observed under an optical microscope (magnifications: 100×, 2000×).
2.6. Molecular Characterization and Taxonomy
Four monosporic isolates were grown on PDA for 7 days for collecting mycelium, which was freeze-dried and ground to a fine powder with the Tissue Lyser System® (Qiagen, Les Ulis, France). For the fungal DNA extraction, the NucleoMag 96 Plant Macherey-Nagel Kit (Macherey-Nagel Gmbh & Co. KG, Dueren, Germany) was used according to the supplier’s instructions. Briefly, 500 µL of MC1 lyse buffer and 10 µL of RNAse were added to 50 mg of ground mycelium, then vigorously vortexed. The samples were incubated for 30 min at 56 °C, centrifuged at 16,000× g for 20 min. Meanwhile, a plate was prepared within the first line, 100 µL of the binding buffer MC2 and 15 µL of the NucleoMAg c-Beads were added into each well. In the wells of the second line, 200 µL of washing buffer MC3 was added. In the wells of third line, 200 µL of washing buffer MC4 was added. In the wells of the fourth line, 200 µL of an 80% solution of EtOH was added, 200 µL of washing buffer MC5 in the fifth line and, finally, 80 µL of MC6 elution buffer in the last line. In total, 100 µL of each sample solution was added in the wells of the first line of the plate and the latter was positioned into the MagMaxTM Express Robot (Applied Biosystems, Espoo, Finland). The extracted DNA was finally eluted in the last line of the plate. The quality and quantity of the extracted DNA were assessed both by 1% agarose gel electrophoresis and by UV spectrophotometry using a nanodrop® ND 1000 spectrophotometer (Labtech International LTD©, Uckfield, UK).
Further identification of
Fusarium species was performed by PCR amplification targeting the nucleotide sequences of the transcribed spacer sites (ITS) and the β-tubulin (
β-tub) gene. The amplification of these loci was carried out with the primers listed in
Table 1. The PCR mix contained 15.25 µL of PCR-grade water, 5 µL of KAPA HIFI Buffer (5×); 0.75 µL of 10 mM KAPA dNTP Mix, 0.75 µL of each primer at 10 µM, 2 µL of the template DNA at 20 ng µL
−1, and 0.5 µL of 1 U µL
−1 of KAPA HIFI DNA polymerase for a total reactional volume of 25 µL. The PCR cycle was conducted as follows: 3 min at 95 °C for the initial denaturation, followed by 25 cycles of 20 s at 98 °C for the denaturation phase, 45 s at the primer’s annealing temperature (58 °C), 60 s at 72 °C for the elongation and, finally, 2 min at 72 °C for the final elongation.
The PCR product obtained was sequenced by the company GENEWIZ (Leipzig, Germany). Nucleotide sequences were aligned using the Clustal W algorithm in BioEdit 7.0 software. Sequence similarity searches were performed with BLAST (basic local alignment search tool) against NCBI public database (
www.ncbi.nlm.nih.gov/genbank, 15 March 2022). Further, dendrograms were constructed using the MEGA-X program (MEGA-X: Molecular Evolutionary Genetics Analysis version 10.0.5 (Tamura, Stecher, and Kumar, 1993–2020) and original sequences of target species and nucleotide sequences (target and other species of the genus
Fusarium) from the NCBI database were used: original nucleotide sequences of DNA sites (Beta Tubulin)—
F. acuminatum (MH341248),
F. avenaceum (EU357849),
F. tricinctum (MK936369),
F. culmorum (KP765705), and
F. graminearum (MN416026). In addition,
Aspergillus carbonarius (HE577803) was used as an outer group. The sequences of the four isolates from this study have the following numbers in GeneBank: 3T = ON128289, 4T = ON128290, 32T = ON128291, 33T = ON128292. The data are presented as a consensus phylogenetic tree using the unweighted pair group (UPGMA) method. Branches corresponding to partitions reproduced in less than 50% bootstrap replicates are collapsed. The percentage of replicate trees in which the associated taxa clustered together in the bootstrap test (100 replicates) are shown next to the branches. The evolutionary distances were computed using the Maximum Composite Likelihood method and are in the units of the number of base substitutions per site. This analysis involved 10 nucleotide sequences. Codon positions included were 1st + 2nd + 3rd + Noncoding. All ambiguous positions were removed for each sequence pair (pairwise deletion option).
2.7. In Vitro Growth and Production of Enniatins in Agar Media
Plugs were taken from each previously prepared monosporal culture and incubated in liquid CMC medium (15 g carboxymethyl cellulose, 1 g yeast extract, 0.5 g MgSO
4·7H
2O, 1 g NH
4NO
3, 1 g KH
2PO
4, 1 L distilled water) for 48 h to induce sporulation. Ten µL of 10
6 mL
−1 spore suspension was inoculated on 10 mL of PDA or FDM-agar, which was previously described as an ENNs-inducing medium [
18]. The FDM-agar medium composition was: 12.5 g of glucose, 4.25 g of NaNO
3, 5 g of NaCl, 2.5 g of MgSO
4·7H
2O, 1.36 g of KH
2PO
4, 0.01 g of FeSO
4·7H
2O, 0.0029 g of ZnSO
4·7H
2O, 15 g of agar, 1 L of distilled water. The cultures were incubated for 11 days and the growth was measured as the surface covered by the mycelium using ImageJ software. The mycotoxins were extracted on the last day of culture. The plate content (agar medium and mycelium) was sliced and placed into 35 mL ethyl acetate (VWR, Fontenay-Sous-Bois, France) for 15 min at room temperature rotating end-over-end at 250 rpm and filtrated on No 4 Whatman filter paper. Five mL were evaporated to dryness at 45 °C under a gentle nitrogen flow. The dried samples were resuspended with 200 µL of methanol/water (1:1,
v/v) and filtered on 0.2 µm filter before ENNs’ analysis using the HPLC-DAD method as in
Section 2.4.
2.8. In Vitro Growth and Production of Enniatins in Liquid FDM
Alternatively, for assessing the production of ENNs, liquid cultures in FDM were also used as in Gautier et al. [
4], with incubation for 11 d at 25 °C. After centrifugation at 5000×
g and filtration, 4 mL was sampled and 8 mL of ethyl acetate was added in 15 mL PTFE tubes. The mixture was vortexed for 2 min and agitated for 15 min at 250 rpm as above. Then, 5 mL of the supernatant was evaporated to dryness at 45 °C under a nitrogen flow. The dried samples were dissolved with 200 µL of methanol/water (1:1,
v/v) and filtered on 0.2 µm filter before ENNs’ analysis using the HPLC-DAD method as in
Section 2.4. The mycelium collected after centrifugation was freeze-dried and weighted.
2.9. Assessment of the Fusarium Susceptibility to Essential Oils
The effects of EOs from eight Tunisian plants (Ammoides pusilla, Artemisia absintum, Carum carvi, Mentha spicata, Myrtus communis, Origanum vulgare, Schinus terbentofonius, Thymus capitatus) on the mycelial growth and production of ENNs by one of the isolates, F. acuminatum 33T, were measured in FDM-agar as described by Chakroun et al. [
15] and in
Section 2.7. Briefly, the EOs were diluted at 0.1 µL mL
−1 in FDM-agar medium poured into 90 mm Petri dishes. After central inoculation with a spore suspension and incubation for 10 d at 25 °C, the surface colonized by the mycelium was measured and the contents of the plates were collected for ENNs’ extraction and analysis using the HPLC-DAD method.
2.10. Statistical Analyses
Mycelial growth and ENNs concentrations were analysed by ANOVA and Duncan’s multiple range tests using SAS Software (Statistical Analysis System, version 9, Cary, NC, USA). Differences were considered at a significance level of 95% (p < 0.05).
4. Discussion
The dry climatic conditions around the anthesis period of the years 2017 and 2018 in Northern Tunisia (Béjà) were not conducive to the development of FHB, and no symptoms were recorded on the experimental parcels used for characterizing the 13 wheat cultivars sampled in this study. In our attempt to isolate
Fusarium sp. from these asymptomatic harvested grains, only one sample was positive, and isolates of
F. culmorum and
F. acuminatum were obtained. This sample was also the only one containing DON contamination. The presence of TCTB in asymptomatic grains is currently observed. In a Spatio-temporal model of the multifaceted virulence strategy deployed by the advancing
F. culmorum, it was proposed that asymptomatic infection occurs with high induction of the TRI genes involved in DON biosynthesis and accumulation [
21]. The obtained strain of
F. culmorum was probably responsible for the DON accumulation in the grains studied in the present work.
The colonization of spikes by at least two FHB pathogens producing the same or different mycotoxins is a common observation. Audenaert et al. [
22] reported a clear association between
F. poae producing NIV and
F. avenaceum producing ENNs in symptomatic ears collected in Flanders in 2007. However, the co-occurrence of
F. acuminatum with
F. culmorum in wheat grains is not a common observation since
F. acuminatum is infrequently found in wheat grains.
Fusarium species have been divided into 23 informal multispecies lineages, termed species complexes [
23].
Fusarium acuminatum is a member of the
F. tricinctum species complex along with
F. avenaceum and
Fusarium tolurosum as well as other species. The members of the
F. tricinctum species complex have a wide geographic distribution and can occur on extremely diverse plants, often without causing severe disease [
5]. They are classified as FHB contributors but also as causing agents of
Fusarium foot rot.
Fusarium acuminatum is known to determine significant reductions in the germination ratio and vegetative vigor of durum wheat seedlings [
24] and as one of the causing agents of dryland root rot of winter wheat in Colorado [
25]. It exhibited weak aggressiveness on wheat seedlings and had a mean crown rot activity in China where significant correlations of its occurrence in diseased wheat stems with global climatic variables were observed [
26].
Fusarium acuminatum isolates were weakly pathogenic in an FHB pathogenicity assessment on different durum wheat varieties in Tunisia [
6].
The obtained isolates were identified by both morphological and molecular tools (
Figure 1,
Figure 2 and
Figure 3). Overall, the
β-tub gene site was more effective in distinguishing and identifying the species under study than the ITS. The morphologic identification of two isolates of
F. acuminatum conducted in this work was in line with the findings of Logrieco et al. [
27] who identified a slow-growing type of
F. acuminatum with carmine-red pigmentation and the production of heterogeneous macroconidia (mostly three to four septa). Lesli and Summerell [
17] also described
F. acuminatum as a relatively slow-growing species and mentioned the formation of red pigments, sometimes brown, in the agar and that the presence of macroconidia with three and four septa was not uncommon [
18]. The pigment formation was confirmed by Burgess and Forbes [
28]. The abundant production of microconidia was also described in the work of Rabie et al. [
29].
Fusarium acuminatum has been recovered from cereals in Canada, North Carolina, and Mediterranean countries, but at a lower frequency compared to
F. avenaceum and
F. tricinctum [
30,
31,
32]. In Italy,
F. acuminatum was reported to be among the most harmful
Fusarium species for durum wheat production causing
Fusarium foot rot. It was detected within 50% of the analyzed soils in Sicily and seemed not to be affected by the suppressive effects of biofumigation with brassicaceous green manures [
33]. Studying
Fusarium species colonizing the lower stems (crowns) of bread and durum wheat from different regions of Turkey, Gebremariam et al. [
34] isolated
F. acuminatum with a frequency of 14%, mostly related to crown rot. The members of the
F. tricinctum species complex are also contributors to FHB.
Fusarium acuminatum has been isolated from Italian durum wheat grains from three cultivation areas [
31], and from symptomatic wheat and barley grains [
32]. In this latter study, the authors identified
F. acuminatum isolates from Italy (growing season 2017–2018), using molecular tools. In a previous study, when collecting wheat grains on FHB symptomatic spikes at the filling stage from 11 fields in Northern Tunisia during the 2004 and 2007 crop seasons,
F. acuminatum was found in four different fields with always low percentages compared to the most common
Fusarium species, these being
F. culmorum,
F. avenaceaum, and
F. equiseti [
6].
Fusarium acuminatum was not detected in other studies dealing with Tunisian wheat grains [
6,
7,
8]. It was rarely found in other Tunisian grains such as sorghum in a study where 1 out of 53
Fusarium sp. isolates identified was related to
F. acuminatum [
35]. Due to the scarcity of information about
F. acuminatum in wheat grains in Tunisia, its potential as a harmful
Fusarium species was highlighted by observations in the Mediterranean conditions in Sicily [
33], and its capacity to produce emerging mycotoxins (Beauvericin, ENNs, Fusaproliferin, and Moniformin) [
5], it was of concern to characterize the production of at least one of these mycotoxins by the isolates we obtained from a Tunisian durum wheat sample.
In our study, ENA and ENB1 co-occurred with DON in the wheat sample from which the strains of
F. acuminatum were isolated. However, ENNs were detected in all the wheat cultivars in the two growing seasons (
Table 1), and the highest ENNs levels were found in the sample of the Khiar variety contaminated with DON, these being 524 and 41 mg Kg
−1 for ENA and ENB1, respectively. When investigating the presence of ENNs, BEA, and FUS in cereals and derived products from Tunisia, Oueslati et al. [
10] found also that all the analyzed wheat samples were contaminated with ENNs, at a maximum concentration of 532 mg Kg
−1. Using the same extraction procedure and LC-DAD analysis on breakfast and infant cereals from Morocco, Mahnine et al. [
36] found a maximum total ENNs value of 1264 mg Kg
−1. Studies on ENNs’ contamination in wheat grains and wheat products published recently were most of the time performed using quantification by LC-MS/MS in multi-mycotoxin analysis and reported quite lower levels than in works using LC-DAD analysis. Investigating 470 bread wheat and 260 durum wheat samples from the French harvests of 2012, 2013, and 2014, and using a quantification by LC-MS/MS, Orlando et al. [
37] found an occurrence of ENNs ranging from 53% (2014) to 91% (2012), and mean values ranged from 47 to 142 µg Kg
−1 for bread wheat and from 55 to 596 µg Kg
−1 for durum wheat. In a long-term field survey using HPLC-QqQ-MS/MS in The Netherlands, ENA1, ENB, and ENB1 were detected in 14.2%, 46.6%, and 26.2% of the analyzed samples, respectively [
38]. In Algeria, 21 out of 30 (70%) wheat samples were contaminated with ENB1 at concentrations from 19 to 4569 µg Kg
−1, and seven samples were contaminated with ENA at concentrations ranging from 8 to 88 µg Kg
−1 [
39]. ENA1 and ENB were also detected in many samples. In the present study on asymptomatic grains, no ENNs were detected using quantification by LC-MS/MS in samples showing concentrations of ENA ranging from 320 to 930 mg Kg
−1 when the LC-DAD method was used. This agrees with the absence of
Fusarium sp. isolation. Metabolites extracted from grains may have interfered with the quantification of ENNs, and data have to be used with caution.
Despite the uncertainty of the accumulation of ENNs in the grains, the studied isolates identified as
F. acuminatum proved to be able to produce three ENNs in vitro, ENA1, ENB, and ENB1 but not ENA (
Figure 4). The difference in distribution between the four ENNS in naturally contaminated grains and in liquid or agar culture media may be due to differences in the regulation of the synthesis in various environments. In different works,
F. acuminatum has been reported to be capable of producing ENA, A1, B, B1, B2, B3, B4, P1, and P2 [
40]. Our results on ENNs’ production agree with those of Senatore et al. [
32] who studied five strains of
F. acuminatum from a culture collection and four new ones isolated in 2017–2018 from symptomatic wheat and barley grains in Italy. When incubated in vitro on rice for 10–12 days in the dark at 25 °C, ENB and ENB1 were detected at similar concentrations, and ENA1 at lower concentrations (1/3 that of ENB or ENB1 for six strains), but no ENA was detected. The results we obtained with two Tunisian strains of
F. acuminatum, 32T and 33T, agree with this distribution of ENNs, both in liquid and agar media. In a previous work where
F. acuminatum 33T was cultivated on FDM-agar medium, its level of ENNs’ production was 10-fold higher than for a strain of
F. avenaceum cultivated under the same conditions [
14]. Comparing the single
F. acuminatum strain with 30
F. avenaceum they isolated in a survey of barley and wheat fields in Paraná state, Brazil, Peirera et al. [
41] found
F. acuminatum to be the strongest producer of ENNs. Despite its low occurrence,
F acuminatum has to be considered as a significant source of mycotoxin contamination of crops, due to its high potential for ENNs’ production.
The antifungal activity of the same eight EOs from Tunisian plants used (
Figure 5) here was previously tested against a strain of
F. avenaceum, which was significantly more affected by AP and TC EOs than by the other EOs [
15], as
F. acuminatum 33T was in the present study (
Figure 5). The mycelial growth inhibiting effect of TC EO was higher than that of AP EO for both species. The same level of inhibition of ENNs’ accumulation in the FDM-agar medium by
F. acuminatum 33T was observed here for both EOs, whereas AP EO was more effective than TC EO for
F. avenaceum [
15]. The effectiveness of AP and TC EOs on two members of the
F. tricinctum complex is a strength for their putative use for controlling these ENN producers and limiting the accumulation of the mycotoxins in plant products. The EOs represent promising biosourced products for the development of natural and eco-friendly alternatives to synthetic fungicides that are currently used. However, practically, the application of crude EOs in the field or at grain storage faces several limits. The production of EOs is limited by the extraction yield from aromatic plants and scaling-up would involve the production of large amount of plant material. New extraction methods with higher yields are now available. Subcritical water extraction (SWE) avoids the loss and degradation of volatile and thermolabile compounds, is low cost, and has favorable environmental impacts [
42]. Another limit is that essential oils are very volatile substances and are sensitive to the exposure to oxygen in the air and to UV light [
43]. The development of a system that protects the EOs from the oxidation and increases the evaporation time is necessary to potentialize them as biofungicides. Encapsulation of the essential oils in different matrixes has been studied to reach this aim. This method can improve their antifungal activity and increase the release period [
44,
45]. Thus, nanoencapsulation enables the use of lower doses of EOs to obtain the same results as the EOs on a free state. The latter point is primordial for the development of different formulations to potentialize the EOs as the scale-up of their production in the aim of field application is a complicated task. Finally, the determination of the contribution of different compounds constituting an EO in its biological activity provides a better understanding of the different interactions among the compounds and their activity [
15,
44]. Hence, formulations focusing on the mixture of the main active compounds in their synthetic form is a promising area of investigation to provide biofungicide alternatives.
It is worth mentioning that, as with other cyclodepsipeptide analogs, ENNs are involved in plant–pathogen interactions, and they are detected in a range of foods or feeds originating from many countries. As they belong to the mycotoxin group, they may be dangerous for human health, but they also possess antimicrobial, insecticidal, antifungal, and antibiotic activities, which may help to develop new drugs, and due to their cytotoxicity, they may be applied in anticancer future therapies [
40].
Fusarium acuminatum 32T and 33T are good candidates for producing ENNs in large quantities for medical applications.