Molecular diagnostics on the toxigenic potential of Fusarium spp. plant pathogens

Authors


Abstract

Aims

We propose and test an efficient and rapid protocol for the detection of toxigenic Fusarium isolates producing three main types of Fusarium-associated mycotoxins (fumonisins, trichothecenes and zearelanone).

Methods and Results

The novel approach utilizes partially multiplexed markers based on genes essential for mycotoxin biosynthesis (fumonisin—fum6, fum8; trichothecenes—tri5, tri6; zearalenone, zea2) in Fusarium spp. The protocol has been verified by screening a collection of 96 isolates representing diverse species of filamentous fungi. Each Fusarium isolate was taxonomically identified through both molecular and morphological techniques. The results demonstrate a reliable detection of toxigenic potential for trichothecenes (sensitivity 100%, specificity 95%), zearalenone (sensitivity 100%, specificity 100%) and fumonisins (sensitivity 94%, specificity 88%). Both presence and identity of toxin biosynthetic genes were further confirmed by direct sequencing of amplification products.

Conclusions

The cross-species-specific PCR markers for key biosynthetic genes provide a sensitive detection of toxigenic fungal isolates, contaminating biological material derived from agricultural fields.

Significance and Impact of the Study

The conducted study shows that a PCR-based assay of biosynthetic genes is a reliable, cost-effective, early warning system against Fusarium contamination. Its future use as a high-throughput detection strategy complementing chemical assays enables effective targeted application of crop protection products.

Introduction

The numerous plant pathogens of the genus Fusarium are responsible for significant losses in crop yield due to both loss of biomass and accumulation of mycotoxins in infiltrated parts. The major toxic compounds synthesized by divergent Fusarium isolates include the following: zearalenone, fumonisins, trichothecenes and their derivatives (D'Mello et al. 1999). While there is a growing body of work documenting biological significance of additional, emergent toxins (e.g. butenolide, fusarins, equisetin, beauvericin and enniatins), their estimated economic and biomedical importance is considerably lower (Desjardins and Proctor 2007).

Notably, the above-mentioned major toxins (fumonisins, trichothecenes, zearalenone and derivative compounds) are frequently not inactivated during food/feed processing and can be present in a masked form (plant-formed conjugates, i.e. glucosides, which can be activated by mammal gut microbiota—e.g. Berthiller et al. 2013; Dall'Erta et al. 2013), increasing health risks to farm animals and humans (Creppy et al. 2002). As more research results are collected, the estimates of health and economical risks (associated with long-term masked mycotoxin exposure) are revised upwards. The updated estimates lead to increasingly restrictive norms for toxin content for food and feed (e.g. European Commission Recommendation 2006/576/EC proposing norms for ochratoxin A, T-2 and HT-2 toxins as well as deoxynivalenol and zearalenone). This only serves to increase a need for efficient and quick methods of assessing possible sources of contamination, preferably by preventing losses in crop yield, via good farming practices including effective fungicide treatments.

The genetic determinants of fumonisin, trichothecene and zearalenone biosynthesis have been characterized in multiple plant pathogenic taxa. Characterization of both core biosynthetic genes (polyketide synthases, trichodiene synthase) and key accessory genes (such as transcription factors or key processing enzymes) enables construction of toxigenicity assays directly targeting the genetic basis of toxin production and accumulation. At the same time (Stepien et al. 2011), the biosynthetic gene alleles exhibit significant interspecific differences, which makes them useful for precise identification of infectious species/populations.

The zearalenone biosynthetic cluster spanning 25 kb of the genomic sequence has been characterized in Fusarium graminearum (Kim et al. 2005), with four principal genes required for toxin biosynthesis (zea1, zea2, zeb1, zeb2) and 3 other genes regulated in conjunction with zeb2 expression patterns (FG02394, FG02399 and FG012015—uncovered by qRT-PCR experiments described by Lysøe et al. (2009)).

Conversely, trichothecene biosynthesis constitutes a multistage process, controlled by at least 12 essential genes, forming a 25-kb-long cluster in F. graminearum (Brown et al. 2001; Kimura et al. 2003). The trichothecene cluster is linked to a key tri5 gene encoding trichodiene synthase, however, four genes segregate at separate loci (notably tri13 and tri14 controlled by a transcription factor encoded by tri10—Tag et al. (2001)). To date, the main cluster has been extensively characterized with numerous studies targeted especially at F. graminearum and F. sporotrichioides species (Kimura et al. 2007), as well as some members of the genus Trichoderma (Cardoza et al. 2011). There is considerable evidence for complex gene relocation scenarios underlying chemotype diversification leading to extant trichothecene type-A- and type-B-producing species (Proctor et al. 2009).

In the past decade, the fumonisin cluster structure (16 gene cluster spanning 42 kb length) has been determined for three toxigenic Fusarium species: F. verticillioides, F. oxysporum (FRC O-1890 strain) and F. proliferatum (Proctor et al. 2008). The interspecies differences between individual biosynthesis-related sequences encompass up to 20% of constituent residues. Notably larger differences are found in gene-flanking regions, an observation which suggests divergent evolutionary paths for cluster copies in different species. Here, the difference in species history and gene phylogeny has been attributed to complex birth/death evolution of the cluster (with independent sorting of copies) and/or horizontal gene transfer events (Proctor et al. 2013). During fumonisin biosynthesis, substitutions of polyketide synthase and/or termination factor can lead to significant changes in the specificity of polyketide condensation for fumonisin analogs (Zhu et al. 2008; Li et al. 2009).

As the broad, genetic basis of the biosynthetic pathway for three major Fusarium mycotoxins is known and multiple exemplar sequences are readily available, it is now possible to develop targeted diagnostic solutions. Through utilizing knowledge about disparate species for the design of degenerate cross-species-specific primers, it is possible to target well-conserved parts of coding sequence (corresponding to conserved parts of protein sequence). Especially for core, secondary metabolite biosynthetic genes, these regions of the coding sequence are unlikely to change in toxin-producing isolates (corroborated by recent evidence for purifying selection in secondary metabolism genes—e.g. Baker et al. 2012).

Current studies on the variability and diversity of the fungal populations make use of various genetic markers, such as the translation elongation factor (tef-1α) and internal transcribed spacer (ITS1/2), employed in assays of the genus Trichoderma (Chaverri et al. 2003; Blaszczyk et al. 2011) and conservative fragments of the genome such as a calmodulin gene (CaM) in Trichoderma and Fusarium populations (Chaverri et al. 2003; Mulè et al. 2004). Also, mitochondrial DNA (mtDNA) is used as a marker of genetic variation. Its relatively short length and the presence of conserved and variable regions allow the identification of closely related species (Ma and Michailides 2007). The sequence of the large subunit of the RNA polymerase II (Hibbett et al. 2007) can also be used to distinguish between divergent phytopathogenic species. Among so many molecular markers, the translation elongation factor (tef-1α) appears to be the most useful in taxonomic studies of fungi, especially in the genus Fusarium (Geiser et al. 2004; Kristensen et al. 2005). Recently, more attention is devoted to markers directly involved in the secondary metabolism (Proctor et al. 2009). Many researchers use genes from the FUM cluster as a good additional marker for phylogenetic and taxonomic studies of the fumonisin-producing Fusarium species (González-Jaén et al. 2004; Baird et al. 2008; Stepien et al. 2011).

The current line of research for the detection of toxigenic species involves simultaneous use of multiple genes belonging to different clusters responsible for toxin production, for example mPCR assays detecting aflatoxigenic, trichothecene- and fumonisin-producing and ochratoxigenic fungal isolates (Rashmi et al. 2013). The recent studies also aim to combine qualitative and quantitative methods for detecting the toxigenic potential. One of the approaches, based on multiplex real-time PCR, is able to detect and quantify mycotoxigenic species in cereal grains with the use of markers targeting the trichothecene synthase (tri5) gene in trichothecene-producing Fusarium sp. isolates, the rRNA gene in Penicillium verrucosum and the polyketide synthase gene (Pks) in Aspergillus ochraceus (Vegi and Wolf-Hall 2013).

The problem addressed in the proposed work was to design and standardize a diagnostic tool allowing the identification of toxigenic Fusarium isolates producing fumonisin B1, trichothecenes and zearalenone. The new protocol is applicable for both in vitro and field samples, with resolution sufficient for direct sequencing of amplified sequences.

Materials and methods

Fungal isolates and field samples

Fungal isolates originated from the culture collections of the Institute of Plant Genetics (Polish Academy of Sciences, Poznan, Poland). The isolates originated from soil, infected cereal grain samples and buildings infested by fungal pathogens. To avoid contamination of fungal cultures with cryptic species, which are hard to distinguish with traditional morphological methods, isolates were purified using single-spore culturing (Leslie and Summerell 2006). Scabby kernels were plated on small nutrient agar (SNA) medium in Petri dishes, and taxa were morphologically identified using an optical microscope (Olympus, Center Valley, PA) at 400–500 × magnification, according to the manual of Leslie and Summerell (2006). Mycelia of isolates cultivated on potato dextrose agar (PDA) were used for DNA isolation. All 96 isolates were identified with at least one molecular marker (ITS 1/2 and/or tef-1α marker), and species assignment was carried out through comparison with reference sequences in NCBI/GenBank and Fusarium-ID (Geiser et al. 2004). Assignment of species to monophyletic complexes was based on the recent taxonomic and phylogenetic research conducted by O'Donnell et al. (2013).

DNA extraction from fungal cultures and field samples

Fungal cultures

Mycelium used for DNA extraction was grown in Czapek-Dox broth (Sigma-Aldrich, St Louis, MO) with yeast extract (Oxoid, Waltham, MA) and streptomycin sulphate (50 mg l−1; AppliChem, Darmstadt, Germany) and after incubation at 25°C for 21 days on a rotary shaker (100 g). Mycelium was collected on filter paper in a Büchner funnel and freeze-dried. Total DNA was extracted using the CTAB method (Doohan et al. 1998). The quality of DNA was estimated by NanoDrop 2000 UV-Vis Spectrophotometer (Thermo Scientific, Wilmington, NC) and via Experion Automated Electrophoresis System (Bio-Rad, Hercules, CA).

Field samples

Infected wheat chaffs and kernels (2012, Parabola cultivar) were ground to fine powder, and DNA was obtained using the DNase kit (Qiagen, Hilden, Germany).

Primer design

The degenerate, cross-species-specific primers were designed on the basis of backtranslated codon alignments created from protein sequence alignments of homologous genes from NCBI/RefSeq release ver. 56 (Pruitt et al. 2012) and NCBI/GenBank release ver. 194 (Benson et al. 2013) and Ensembl/Fungi (Flicek et al. 2012) release 18. Protein alignments for fum8, fum6, zea2, tri5 and tri6 genes were obtained with MAFFT-LINSI (Katoh and Toh 2010), subsequently backtranslated and screened for primers with Python scripts. Primer sequences were screened against propensity for homodimer and heterodimer formation on the basis of nearest-neighbour energy/melting temperature calculations with both IDT OligoAnalyzer and in-house Python scripts implementing nearest-neighbour enthalpy/entropy calculations described by SantaLucia (1998) with corrections based on Owczarzy et al. 2008.

PCR amplification

The PCR was carried out in a 25 μl reaction mixture containing the following: 1 μl of DNA (50 ng μl−1), 12·5 μl PCR buffer (50 mmol l−1 KCl, 1·5 mmol l−1 MgCl2, 10 mmol l−1 Tris-HCl, pH 8·8, 0·1% TritonX-100), 1U polymerase (Sigma-Aldrich), l0 mmol l−1 dNTP (Invitrogen, Carlsbad, CA), 0·5 μl 100 mmol l−1 of each primer and 11·5 μl H2O. Amplifications were performed in C1000 Touch™ Thermal Cycler (Bio-Rad) under the following conditions: initial denaturation 5 min at 94°C, 35 cycles of 45 s at 94°C, 45 s at 53–56°C (Table 1), 1 min at 72°C and for the final extension 10 min at 72°C. Amplification products were separated on a 1·5% agarose gel (Invitrogen) in 1 × TBE buffer (0·178 mol l−1 Tris-borate, 0·178 mol l−1 boric acid, 0·004 mmol l−1 EDTA) and stained with ethidium bromide. The 10 μl PCR products were combined with 2 μl of loading buffer (0·25% bromophenol blue, 30% glycerol). A 100-bp DNA LadderPlus (Fermentas, St. Leon-Rot, Germany) was used as a size standard. PCR products were electrophoresed at 3 Vcm−1 for about 2 h, visualized under UV light and photographed (Gel DOC EZ Imager; Bio-Rad).

Table 1. The sequences of the primers used for amplification and sequencing
Gene targetedPrimer nameSequences (5′–3′)Estimated product length (base pairs)
Trichodiene synthase (tri5)T5_am_fA1CTY MRR ACM ATY GTN GGC ATG468
T5_am_rA1AVA CCA TCC AGT TYT CCA TYT G
Zinc finger transcription factor (tri6)TRI6_dm_fA2TAT GAA TCA CCA ACW TTC GA526
TRI6_dm_rA1CGC CTR TAR TGA TCY CKC AT
Zearalenone polyketide synthase (zea2)ZEA2_dm_fA1ACM TCA CCA TCM AAR TTC TG340
ZEA2_dm_rA1GCR TCY CKG TAR TCR CTC AT
Oxygenase (fum6)FUM6_dm_fA2CRA CMG AGA TCA TGG TGA C672
FUM6_dm_rA1GTY TCR TGT CCK GCA ATG AG
Oxoamine synthase (fum8)F8_am_fA1GGY TCK TTT GAG TGG TGG C350
F8_am_rA1CRA CWG GAA ARC AKA YRA YGG

Sequencing

The 3-μl PCR products were purified with exonuclease I and shrimp alkaline phosphatase according to Chelkowski et al. (2003). Sequencing reactions were prepared using the ABI Prism BigDye Terminator Cycle Sequencing ReadyReaction Kit in 5 μl volume (Applied Biosystems, Grand Island, NY). DNA sequencing was performed on an ABI PRISM3100 GeneticAnalyzer (Applied Biosystems).

Sequences were edited and assembled using Chromasv.1.43 (Applied Biosystems). clustal w (Thompson et al. 1994) and MUSCLE (Edgar 2004) were used to align the sequences; the resulting alignments were inspected and refined manually. All positions containing gaps and missing data were eliminated from the data set.

Multiplex PCR

The multilplex PCR was carried out in a 25 μl reaction mixture containing the following: 1 μl 50 ng μl−1 of DNA, 4 μl PCR buffer (20 mmol l−1 Tris-HCl, 0·1 mmol l−1 EDTA, 1 mmol l−1 DTT, 100 mmol l−1 KCl, stabilizers, 200 μg/ml BSA and 50% glycerol), 1U polymerase (Thermo Scientific), l0 mmol l−1 dNTP (Invitrogen), 0·5 μl 100 mmol l−1 of each primer and 14·5 μl H2O. To each reaction mixture, 3 μl of Q-Solution was added to avoid primer dimerization. Amplifications were performed in Touch™ Thermal Cycler (Bio-Rad) under the following conditions: initial denaturation 30 s at 98°C, 35 cycles of 5 s at 98°C, 5 s at 55°C, 15 s at 72°C, with the final extension of 1 min at 72°C. Amplification products were separated on 2% agarose gel (Invitrogen) in 1 × TBE buffer (0·178 mol l−1 Tris-borate, 0·178 mol l−1 boric acid, 0·004 mol l−1 EDTA) and stained with Midori Green (Nippon Genetics, Dueren, Germany). A 100-bp DNA LadderPlus (Fermentas) was used as a size standard. PCR products were electrophoresed at 3 Vcm−1 for about 2 h, visualized under ultraviolet (UV) light and photographed (Gel DOC EZ Imager; Bio-Rad).

Determination of trichothecenes concentration

Determination of trichothecenes was performed in solid PDA culture. Briefly, subsamples (1 g of mycelium with medium) were extracted with acetonitrile/water (82 : 18) and cleaned-up on a Myco Sep 227 Trich + column. The group B trichothecenes (DON, NIV, 3AcDON, 15AcDON, FUS-X) were analysed as trimethylsilylsilyl ethers derivatives. After sililation, samples were extracted with isooctane and 1 μl of sample was injected on a GC/MS system. The analyses were run on a gas chromatograph (Hewlett Packard GC 6890, Waldbronn, Germany) hyphenated to a mass spectrometer (Hewlett Packard 5972 A, Waldbronn, Germany), using an HP-5MS, 0·25 mm × 30 m capillary column. The injection port temperature was 280°C, the transfer line temperature was 280°C, and the analyses were performed with programmed temperature. Initial temperature was 80°C held for 1 min, from 80 to 200°C at 15°C min−1 held 6 min and from 200 to 280°C at 10°C min−1, the final temperature being maintained for 3 min. The helium flow rate was held constant at 0·7 ml min−1. Quantitative analysis was performed in single ion monitored mode, and qualitative analysis was performed in SCAN mode (100–700 amu). Recoveries for analysed toxins were as follows: DON 84 ± 3·8%; 3AcDON 78 ± 4·8%; 15AcDON 74 ± 2·2%; FUS X 87%±5·9%; NIV 81 ± 3·8%. Limit of detection was 0·01 mg kg−1.

Determination of zearalenone concentration

Determination of zearalenone was performed in solid PDA medium. Subsamples (1 g of mycelium with medium) were extracted with acetonitrile/water (82 : 18) and cleaned-up on Zearala test affinity columns. Prepared samples were analysed by HPLC consisting of a Waters HPLC 2695 apparatus with a Waters 2475 Multi λ Fluorescence Detector and a Waters 2996 Array Detector (Waters, Milford, MA). Separation was achieved on a 150 mm length × 3·9 mm diameter Nova Pak C-18, 4-μm particle size column and eluted with acetonitrile–water–methanol (46 : 46 : 8, v/v/v) at a flow rate of 0·5 ml min−1. ZEA was detected with a Waters 2475 Multi λ Fluorescence Detector, and the excitation and emission wavelengths were 274 and 440 nm, respectively. Estimation of ZEA was performed by a comparison of peak areas with those of an external standard (>95%; Sigma-Aldrich) or by co-injection with the standard. The detection limit of ZEA was 3 ng g−1. The similar process was used to determine zearalenone concentration in a wheat bioassay (Gromadzka et al. 2009).

Determination of fumonisin B1 concentration

The samples (5 ml of liquid culture) were filtered through Whatman No. 5 (Whatman, Piscataway , NJ) filter paper and dried under nitrogen stream. The residues were dissolved into methanol water (3 : 1, v/v), adjusted to the pH value of 5·8–6·5 by 0·1 mol l−1 KOH water solution and cleaned using a SAX cartridge. The cartridge was conditioned with 5 ml of methanol followed by 5 ml of methanol–water (3 : 1, v/v). FB1 was eluted from the column to a glass collection vial with 10 ml of 1% acetic acid in methanol. The eluate was evaporated to dryness at 40°C under a stream of nitrogen. The cleaned sample was derivatized with OPA reagent (20 mg 0·5 ml−1 methanol diluted with 2·5 ml 0·1 mol l−1 disodium tetraborate (Na2B4O7 × 10H2O), then combined with 25 μl 2-mercaptoethanol) immediately before HPLC analysis by mixing the OPA reagent and the sample in ratio 4 : 1 v/v. After 2 min, the reaction mixture (10 μl) was injected in a HPLC C18 Nova Pak column (3·9 × 150 mm). Methanol–sodium dihydrogen phosphate (0·1 mol l−1 in water) solution (77 : 23; v/v) was adjusted to pH 3·35 with o-phosphoric acid and used as the mobile phase with the flow rate of 0·6 ml min−1. A Waters 2695 HPLC with a fluorescence detector (λEx = 335 nm and λEm = 440 nm, Waters 2475; Waters) was used for analysis.

Benchmarking

Diagnostic quality parameters (sensitivity, specificity and comparison with a naive predictor) were assessed with the open-source software r (ver. 2.15.2) using the caret package (Kuhn 2008). Results of chemotype identification and marker testing were visualized using in-house R scripts dependent on ggplot2 (Wickham 2009).

Results

Sensitivity and specificity of diagnostic markers

Sensitivity and specificity of designed markers (Table 1) were tested on a collection of 96 fungal isolates. The tests took into account divergent Fusarium species (72 isolates) as well as multiple non-Fusarium filamentous fungi (24 isolates) (Fig. 2). The individual performance of markers was as follows: trichothecene biosynthesis (tri5 + tri6, sensitivity 100%, specificity 95%, P-value vs naive classifier: 1·42e-09), zearalenone (zea2, sensitivity 100%, specificity 100%, P-value vs naive classifier: 7·48e-09) and fumonisin (fum6 + fum8, sensitivity 89%, specificity 89%, P-value vs naive classifier: 3·53e-07). The final results show that the protocol can reliably identify the toxigenic potential for all three toxin groups (trichothecenes, zearalenone and fumonisins) with a sensitivity and specificity of over 90%, excepting fumonisin production within the Foxysporum complex (see also 'Discussion').

Confirmation of results via chemical analysis and sequencing

Taxonomic identification of all isolates was confirmed by sequencing and analysis of rDNA internal transcribed spacer (ITS; 95 isolates) and/or translation elongation factor 1 α (tef-1α; 41 isolates) partial sequences (Table 2). The identified Fusarium chemotypes are consistent with the recent knowledge on species-related compounds (Moretti et al. 2013), and in case of all positive markers, those results were confirmed by direct sequencing of the PCR product (Fig. 1; Table S4).

Table 2. Fungal isolates from the collection of the Institute of Plant Genetics PAS (Functional Evolution of Biological Systems Team) used to develop a multiplex PCR. The naming of monophyletic complexes within Fusarium sp. derived from (O'Donnell et al. 2013)
ComplexSpeciesCollection numberSourceYear of isolationChemotypeMolecular identification
Fumonisin B1Trichothecene ATrichothecene BZearalenoneITS1/2tef-1α
  1. a

    Some of F. oxysporum isolates have the capacity to produce small amounts of fumonisin B1.

F. fujikuroi F. proliferatum 1Italy1984+++
F. fujikuroi F. proliferatum 3Canada1982+++
F. fujikuroi F. proliferatum 7Poland1986+++
F. fujikuroi F. proliferatum 18Norway2006++
F. fujikuroi F. proliferatum 21Italy1986+++
F. fujikuroi F. proliferatum 44Poland1993+++
F. fujikuroi F. proliferatum 58USA1993+++
F. fujikuroi F. proliferatum 59Poland1999+++
F. fujikuroi F. proliferatum 66Poland1999+++
F. fujikuroi F. proliferatum 82Poland2006++
F. fujikuroi F. proliferatum 84Poland2006+++
F. fujikuroi F. proliferatum 85Norway2006+++
F. fujikuroi F. proliferatum 99Italy1993+++
F. fujikuroi F. proliferatum 111Poland2008++
F. fujikuroi F. proliferatum 113Poland2008+++
F. fujikuroi F. proliferatum 141Poland2010+++
F. fujikuroi F. proliferatum 142Poland2011+++
F. fujikuroi F. subglutinans 60Poland1984++
F. fujikuroi F. succisae 4Poland1996++
F. fujikuroi F. temperatum 151Poland1987++
F. fujikuroi F. proliferatum 13Poland1988++
F. fujikuroi F. verticillioides 16Poland1987++
F. fujikuroi F. verticillioides 17Poland1987++
F. fujikuroi F. verticillioides 23Poland1982+++
F. fujikuroi F. verticillioides 29Poland1985+++
F. fujikuroi F. verticillioides 43Poland1986++
F. fujikuroi F. verticillioides 45Poland1982+++
F. fujikuroi F. verticillioides 71Poland1986++
F. fujikuroi F. verticillioides 75Poland2010++
F. fujikuroi F. verticillioides 79Poland2010++
F. fujikuroi F. verticillioides 88Poland1982++
F. fujikuroi F. xyllarioides 67Guinea1985++
F. incarnatum-equiseti F. equiseti 72Poland2010+++
F. oxysporum F. oxysporum 19Poland2010+a++
F. oxysporum F. oxysporum 55Poland1997+a+
F. oxysporum F. oxysporum 57Poland2010+a++
F. oxysporum F. oxysporum 62Poland2010+a+
F. oxysporum F. oxysporum 65Poland1984+a+
F. oxysporum F. oxysporum 69Poland2010+a+
F. oxysporum F. oxysporum 115Poland2010+a+
F. oxysporum F. oxysporum 131Poland2010+a+
F. sambucinum F. cerealis 33Poland1998+++
F. sambucinum F. cerealis 41Poland1986+++
F. sambucinum F. cerealis 87Poland1987+++
F. sambucinum F. culmorum 48Poland1984+++
F. sambucinum F. culmorum 49Poland1997+++
F. sambucinum F. culmorum 70Poland2010+++
F. sambucinum F. culmorum 90Poland1982+++
F. sambucinum F. culmorum 93Poland1986+++
F. sambucinum F. graminearum 52Poland1986+++
F. sambucinum F. graminearum 76Poland1986+++
F. sambucinum F. graminearum 144Poland2011+++
F. sambucinum F. graminearum 149Poland1986+++
F. sambucinum F. poae 12Poland1987++
F. sambucinum F. sporotrichioides 8Poland1999+++
F. sambucinum F. sporotrichioides 32Poland2010+++
F. sambucinum F. sporotrichioides 39Poland2010+++
F. sambucinum F. sporotrichioides 54Poland1993+++
F. sambucinum F. sporotrichioides 106Poland2010+++
F. sambucinum F. sporotrichioides 116Poland2010+++
F. sambucinum F. sporotrichioides 119Poland2010+++
F. tricinctum F. avenaceum 68Poland2010++
F. tricinctum F. avenaceum 105Poland2010+
F. tricinctum F. avenaceum 108Poland2010++
F. tricinctum F. avenaceum 114Poland2010++
F. tricinctum F. avenaceum 117Poland2010+
F. tricinctum F. avenaceum 120Poland2011++
F. tricinctum F. avenaceum 132Poland2011+
F. tricinctum F. tricinctum 14Poland2011+
F. tricinctum F. tricinctum 31Poland1986+
F. tricinctum F. tricinctum 109Poland2010+
F. solani F. solani 6Poland1997+
NA Alternaria alternata 129Poland2010++
NA A. alternata 139Poland2010++
NA Alternaria brassicicola 128Poland2010++
NAAlternaria sp.97Poland2010++
NA Aspergillus niger 148Poland2010++
NA Clonostachys rosea 20Poland2010+
NAClonostachys sp.104Poland2010+
NA Penicillium commune 136Poland2010+
NA P. commune 138Poland2010+
NA P. herbarum 137Poland2010+
NA Trichoderma aggressivum 100Poland2009++
NA Trichoderma atroviride 98Poland2009++
NA T. atroviride 158Poland2010+
NA Trichoderma hamatum 95Poland2010+
NA T. hamatum 133Poland2010++
NA T. harzianum 5Poland2010++
NA T. harzianum 25Poland2010++
NA T. harzianum 123Poland2010++
NA T. harzianum 125Poland2010++
NA T. harzianum 153Poland2010++
NA T. harzianum 154Poland2010++
NA Trichoderma longibrachiatum 124Poland2010++
NA Trichoderma viridescens 24Poland2010++
NA T. viridescens 96Poland2009++
Figure 1.

Markers used for diagnostics of the toxigenic potential. (Lane M—DNA marker, line 1–4 tri5 marker; line 5–8 tri6 marker; line 9–12 zea2 marker; line 13–16 fum6 marker; line 17–20 fum8 marker; FC—Fusarium culmorum, FG—F. graminearum, FV—F. verticilioides, FP—F. proliferatum).

Chemical analyses have shown that the analysed isolates produce highly varying amounts of toxin. Additionally, in case of F. sporotrichioides, no chemotype (zearalenone/trichothecene biosynthesis) was detected on potato dextrose agar (PDA medium); however, we were able to qualitatively observe accumulation of toxins in a wheat bioassay (Tables S1–S3). This is consistent with reported influence of different carbon sources on toxin production (Jiao et al. 2008) and suggests differentially regulated expression in F. sporotrichioides compared to F. graminearum.

Although no quantitative assay of the type-A trichothecene accumulation was conducted, the genes present in F. sporotrichioides isolates are highly similar to the model F. sporotrichioides counterparts. Notably, polymorphisms in both tri5 and tri6 partial sequences, obtained from direct sequencing, can unambiguously differentiate between trichothecene type-A and type-B producers (F. graminearum, F. culmorum, F. cerealis, F. poae) within the F. sambucinum complex (Fig. 2).

Figure 2.

Results of chemical analyses and molecular diagnostics tested for 96 isolates. The results are grouped by monophyletic complexes within the genus Fusarium reported by O'Donnell et al. (2013). For trichothecene type-A producers (Fusarium sporotrichioides), zearalenone and trichothecene-associated chemotype was qualitatively assayed on rice kernels. Non-specific marker amplification denotes a non-specific band at different height. Marker: (image) n/a; (image) present; (image) non-specific. Toxin: (image) n/a; (image) present.

False-positive results observed in Fusarium xyllarioides and F. succisae were identified as coding sequences corresponding to unrelated genes. In practice, the resulting product band was also visibly different (very weak and of different height) and easily told apart from specific product. In case of zea2, the product of amplification in a single Phoma herbarum isolate was identified as a related gene (reducing polyketide synthase, highly similar to hypothemycin-reducing polyketide synthase from Hypomyces subiculosus; Reeves et al. (2008)). Again, the band was of visibly different height; however, the strength and quality of amplification suggests that zea2 marker could be adapted towards the recognition of different reducing polyketide synthases involved in resorcyclic acid biosynthesis.

Multiplex PCR

Following the assessment of the individual marker performance, the assay was tested and optimized towards multiplexing the PCR. Multiplexing attempts have shown best results for assays over two separate sets of multiplexed markers: zea2 + tri5 + tri6 for the trichothecene/zearalenone and fum6 + fum8 for the fumonisine toxigenic potential (Fig. 3). In case of both detection sets, the amplification of at least one product was taken to confirm the toxigenic potential of pathogens infecting the tested sample.

Figure 3.

Multiplexed PCRs detecting the toxigenic potential of isolates (Lane M––DNA marker, Fusarium graminearum tri5, tri6, zea2, Fusarium verticilioides fum6, fum8).

Field samples

In addition to the standard PCRs conducted on DNA obtained from cultivated isolates, the toxigenic potential was also examined on genetic material obtained directly from infected tissue samples. This resulted in the positive identification of infected wheat kernel samples (Fig. 4); however, this was not successful in samples of the wheat chaff. Multiplex PCRs conducted on diluted samples (500, 50, 5 ng, 500 pg) gave distinct, specific signatures even at the lowest DNA concentration level of 500 pg.

Figure 4.

PCRs detecting the toxigenic potential of diluted environmental samples (tri5––trichothecene marker; tri5/tri6/zea2––trichothecene and zearalenone markers). DNA concentration 500, 50, 5 ng, 500 pg (Lane M––DNA marker).

Discussion

In this study, we present a novel approach to detect the toxigenic potential of various phytopathogenic fungi by partially multiplexed, degenerate primers based on the genes essential for biosynthesis of major Fusarium sp. mycotoxins (fumonisins, trichothecenes and zearalenone). Such tools are especially valuable when updated risk assessments concerning fungal toxin contamination lead to more restrictive norms regulating their acceptable levels in food and/or feed. These trends result in an increase in demand for efficient and rapid methods for the detection and assessment of potential sources of contamination which can be used also as a part of decision support systems (DSS). At the moment, DSS are primarily focused on the observation of the occurrence of pathogens on host plants (Evans et al. 2008), spores in the air (Kaczmarek et al. 2009) or the impact of weather conditions on the life cycles of pathogens (Dawidziuk et al. 2012).

The isolates of the Foxysporum complex constitute a remarkable outlier in the results obtained for fumonisin-producing species. In this case, the trace amounts of fumonisin were found in cultures of several isolates, but mPCR markers were consistently absent. Previous works by Proctor et al. (2008, 2013) demonstrate possible divergent origins of the fumonisin clusters in distinct member species of Foxysporum and Ffujikuroi complexes. Past research also shows that synthesis of the long reduced polyketide mycotoxins is controlled by accessory genes (i.e. fum8) under a scheme which permits complementation by different core/accessory genes (Zhu et al. 2008; —fum8 complementation for control of biosynthesis). As F. oxysporum is a species with high supernumerary chromosome content (c. 25%; Ma et al. 2010) likely stemming from past horizontal transfers, there is a possibility of different/highly divergent genetic basis complementing biosynthesis of low amounts of fumonisins and/or fumonisin-like compounds in the Foxysporum complex. Notably, the molecular and morphological identification of isolates can be a grey area in some cases (e.g. newly characterized cryptic species like F. temperatum—Scauflaire et al. 2011; low resolution of broad barcode markers in complexes of related species—Blaszczyk et al. 2011). Current and future research is poised to demonstrate finer splits in the complexes of closely related species, previously characterized as monophyletic species (O'Donnell et al. 2013). The taxonomic identification is supplemented and supported by differences in chemotype and sequence of biosynthesis-related genes from closely related taxa—a process made easier by markers designed for direct sequencing of amplification products. Nevertheless, the problematic results do not apply to the most important economic, toxigenic Fusarium species occurring in cultivated high-yield crops (e.g. maize—F. verticillioides, wheat—F. graminearum, F. culmorum).

In related research, previously carried out by Rashmi et al. (2013), the researchers focused on diverse isolates (mainly toxigenic and non-toxigenic Fusarium, Aspergillus and Penicillium), demonstrating the applicability of multiplex PCR to detect ochratoxin-, fumonisin- and trichothecene-synthesizing isolates. However, Rashmi and co-workers did not attempt to provide a more detailed taxonomic identification of their cultures. In our approach, each pathogenic isolate was obtained by single-spore technique and its species assigned by both morphological and molecular methods. The test can efficiently detect the presence of the marker gene in five hundred picograms of template and about one infected kernel among hundred uninfected seeds and each obtained product can be validated by direct sequencing. Sensitivity on this level can significantly support the farmers for instance in the appropriate and rational use of fungicide treatments in the field. The developed diagnostic approach can directly be used in biological material obtained from the field (infected kernels) without the need for prior cultivation on artificial media. Unfortunately, such analysis is only possible in infected kernels. The DNA isolated from chaffs is not of sufficient quality to give reliable results, likely due to the presence of PCR inhibitors, such as polysaccharides (e.g. dextran sulphate, alginic acid—Demeke and Jenkins 2010). This could be alleviated by improvement in preparation procedures. There is a possibility of further extending the approach to direct quantitative studies of the mycotoxin-producing pathogens which (up to date) are typically focused on detection of specific fungal producers (F. graminearum, P. verrucosum, A. ochraceus) and not on assessing the toxigenic potential grounded in common genetic basis among related but distinct species (Vegi and Wolf-Hall 2013).

The multiplexed PCR assay used in the protocol allows for the detection of toxigenic potential in many species simultaneously and in a standardized way. The resulting quality of optimized PCRs allows for direct sequencing of amplification products. Additionally, the low cost (relative to HPLC analysis) of the assay allows easy coupling with simple, targeted techniques (e.g. ELISA) to quickly confirm presence of a specific toxin. Thus, the method can be easily adapted as early warning against mycotoxin contamination allowing much more effective application of fungicides and can serve as supplement conventional mycotoxin detection techniques. What is also very important is that, through the usage of the direct sequencing of the PCR products, the results from individually cultivated isolates should allow easy characterization of variability and phylogeny of infecting pathogen populations.

Acknowledgements

Research funded by LIDER/19/113/L-1/09/NCBiR/2010 ‘Modelling, prediction and verification of fungal toxin accumulation’ applied research grant.

Conflict of Interest

The authors declare no conflict of interest.

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