Canadian Journal of Plant Pathology
ISSN: 0706-0661 (Print) 1715-2992 (Online) Journal homepage: http://www.tandfonline.com/loi/tcjp20
Fusarium mycotoxins: a trans-disciplinary
overview
Matthew G. Bakker, Daren W. Brown, Amy C. Kelly, Hye-Seon Kim, Cletus
P. Kurtzman, Susan P. Mccormick, Kerry L. O’Donnell, Robert H. Proctor,
Martha M. Vaughan & Todd J. Ward
To cite this article: Matthew G. Bakker, Daren W. Brown, Amy C. Kelly, Hye-Seon Kim, Cletus P.
Kurtzman, Susan P. Mccormick, Kerry L. O’Donnell, Robert H. Proctor, Martha M. Vaughan & Todd
J. Ward (2018): Fusarium mycotoxins: a trans-disciplinary overview, Canadian Journal of Plant
Pathology, DOI: 10.1080/07060661.2018.1433720
To link to this article: https://doi.org/10.1080/07060661.2018.1433720
Accepted author version posted online: 26
Jan 2018.
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Publisher: Taylor & Francis & The Canadian Phytopathological Society
Journal: Canadian Journal of Plant Pathology
DOI: 10.1080/07060661.2018.1433720
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Fusarium mycotoxins: a trans-disciplinary overview
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Subject category : Symposium contribution / Contribution à un symposium
MATTHEW G. BAKKER, DAREN W. BROWN, AMY C. KELLY, HYE-SEON KIM,
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CLETUS P. KURTZMAN, SUSAN P. MCCORMICK, KERRY L. O’DONNELL,
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ROBERT H. PROCTOR, MARTHA M. VAUGHAN AND TODD J. WARD
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USDA Agricultural Research Service, National Center for Agricultural Utilization Research,
Mycotoxin Prevention and Applied Microbiology Research Unit, 1815 N University St, Peoria,
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IL 61604 USA
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Correspondence to : Matthew G. Bakker. E-mail: Matt.Bakker@ars.usda.gov
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Accepted 12 January 2018
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This paper was a contribution to the symposium entitled “ Toxigenic Fusarium Species and Mycotoxins :
Challenges and Perspectives” held during the Canadian Phytopathological Society Annual Meeting in
Winnipeg, Manitoba, June 2017.
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Fusarium mycotoxins: a trans-disciplinary overview
Abstract
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Due to health risks and economic losses associated with mycotoxins produced by plant
pathogenic Fusarium species, there is a compelling need for improved understanding of these
fungi from across diverse perspectives and disciplinary approaches. Phylogenetic studies have
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made tremendous progress in delineating the species that comprise the genus Fusarium, many
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of which are morphologically cryptic. Control of mycotoxin contamination will be facilitated by
accurate species identification and a thorough understanding of the distribution of mycotoxin
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biosynthetic genes among those species. The biochemical pathways leading to the formation of
several Fusarium mycotoxins have been elegantly linked with the genes responsible for each
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chemical transformation during synthesis, and for most structural differences among
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chemotypes. Screens for the biotransformation of mycotoxins have led to the description of
chemical modifications that impact bioactivity and have implications for monitoring and testing
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of the food supply. Population biology studies have revealed the potential for introductions of
foreign genotypes to dramatically alter regional populations of mycotoxigenic fusaria. Genomic
analyses have begun to reveal the complex evolutionary history of the genes responsible for
mycotoxin production, both across and within lineages. Improved understanding of how
climate variability impacts plant-Fusarium interactions and mycotoxin accumulation is
necessary to effective plant resistance. Additionally, improved understanding of interactions
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between Fusarium and other members of crop microbiomes is expected to reveal novel
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strategies for limiting disease and mycotoxin accumulation.
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Introduction
The genus Fusarium (Ascomycota; Sordariomycetes; Hypocreales) is ubiquitous in
agronomic systems around the world and includes many economically important plant
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pathogens. Plant diseases caused by Fusarium include seedling blights and root rots (Bakker et
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al. 2016), vascular wilts (Michielse and Rep 2009), diseases of reproductive tissues and
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developing seeds (Kazan et al. 2012), and storage diseases (Gachango et al. 2012).
Collectively, Fusarium species (fusaria) possess the genetic ability to produce hundreds
of structurally diverse secondary metabolites, most of which have poorly understood or entirely
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unknown ecological functions (Ma et al. 2013; Hansen et al. 2015; Brown and Proctor 2016;
Niehaus et al. 2016; Kim et al. 2017). These metabolites include several toxins that act as
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virulence factors related to plant disease development (Proctor et al. 1995). Of even greater
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concern, however, are the health impacts for humans and livestock that consume grains
contaminated with mycotoxins (Pestka 2010; Wu et al. 2014).
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Among the Fusarium mycotoxins of primary concern are the trichothecenes, fumonisins,
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and zearalenone. Trichothecenes are produced by Fusarium graminearum and its close
relatives, and are associated with Fusarium head blight of small grains as well as ear rot of corn
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(Zea mays). Trichothecenes are epoxide containing sesquiterpenoid compounds that play a
significant role in pathogen virulence in planta, likely due to their ability to inhibit eukaryotic
protein synthesis (Cundliffe et al. 1974; Bai et al. 2001). Zearalenone is an estrogen mimic
(Kowalska et al. 2016) that is produced by F. graminearum and related species within the F.
sambucinum species complex. Zearalenone is not required for disease development on wheat
(Munkvold 2017). Fumonisins are produced by Fusarium verticillioides and some of its close
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relatives, and are associated with ear rot of corn. Fumonisins are polyketide derived mycotoxins
that are not required for disease of maize (Desjardins and Plattner 2000), but have health
impacts related to kidney and liver toxicity and neural tube defects and are probable
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carcinogens due likely to their ability to disrupt sphingolipid biosynthesis (Stockmann-Juvala
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and Savolainen 2008).
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Losses to the agricultural economy that are attributable to mycotoxigenic Fusarium spp.
are valued at hundreds of millions of dollars per year at regional scales (Windels 2000; Nganje
et al. 2004) and likely reach costs of billions of dollars per year globally. Due to the health and
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economic costs of mycotoxins produced by Fusarium spp., there is a compelling need to study
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these fungi from across diverse perspectives and disciplinary approaches.
In this mini-review, we provide a transdisciplinary overview of: i) Fusarium
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phylogenetics; ii) linkages between mycotoxin biosynthetic gene clusters and chemical
structures; iii) biotransformation of mycotoxins to reduce toxicity; iv) Fusarium population
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biology; v) genomics of secondary metabolite production; and vi) mycotoxigenic fusaria in a
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phytobiomes context.
Phylogenetics and classification of mycotoxigenic Fusarium
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First erected by Link (1809), and subsequently validated by Fries (1821), the genus
Fusarium has undergone many taxonomic revisions over the past two centuries. Following the
movement to a ‘one fungus, one name’ system of nomenclature, the research community
expressed strong support for circumscribing the limits of Fusarium to preserve historical use of
the name (Geiser et al. 2013). This circumscription was supported by molecular phylogenetic
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analyses of partial nucleotide sequences for RNA polymerase genes RPB1 and RPB2, which
provided a well-supported phylogenetic hypothesis of evolutionary relationships within the
genus (O'Donnell et al. 2013). Results of this analysis resolved 20 monophyletic species
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complexes and nine monotypic lineages. Two of these monotypic lineages, based on newly
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discovered species, are now recognized as species complexes (Laurence et al. 2011; Zhou et al.
2016).
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Clearly delineating species within the genus Fusarium, and defining the distribution of
mycotoxigenic phenotypes among those species, will greatly facilitate progress toward effective
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control of plant diseases and mycotoxin contamination of food and feed. To support this effort,
more than 14,000 phylogenetically diverse Fusarium strains have been accessioned in the
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Agricultural Research Service (ARS) Culture Collection (Peoria, IL), where they are available for
distribution upon request. Many of these strains have been genetically characterized using
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Genealogical Concordance Phylogenetic Species Recognition (GCPSR; see Sarver et al. 2011), a
robust method for identifying species boundaries (Taylor et al. 2000). To date, GCPSR-based
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studies indicate that approximately half of the ~300 phylogenetically distinct species-level
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Fusarium lineages represented within the ARS Culture Collection are not distinguishable from
other species by morphological traits, and are currently unnamed (Aoki et al. 2014).
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In an effort to enable and promote accurate, species-level identification of Fusarium
isolates, two web-accessible DNA sequence databases (i.e. FUSARIUM-ID and Fusarium MLST)
were developed (Geiser et al. 2004; Crous et al. 2015; O'Donnell et al. 2015). These databases
are frequently updated with sequence data from newly characterized fusaria. To date, portions
of three protein coding genes (translation elongation factor, TEF1; RPB1; RPB2) have been
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shown to be phylogenetically informative at or near the species level across the breadth of
Fusarium (Geiser et al. 2004; O'Donnell et al. 2013). In contrast to GenBank, where many
sequences assigned to Fusarium are misidentified (O'Donnell et al. 2015), all of the sequences
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in the two Fusarium-specific databases were derived from reference strains that can be
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obtained for additional study via the ARS Culture Collection (https://nrrl.ncaur.usda.gov/), the
Fusarium Research Center at Pennsylvania State University (http://www.fusariumdb.org/), or
KNAW).
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Genetics and biosynthesis of Fusarium mycotoxins
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the Westerdijk Fungal Biodiversity Institute (http://www.westerdijkinstitute.nl/; formerly CBS-
Sustained research investments have provided tremendous insights into the genetics
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and biochemistry underlying the biosynthesis of most Fusarium mycotoxins, as well as insights
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into genetic bases for chemotype variation among strains. Here, we use trichothecene
biosynthesis to illustrate the state of knowledge (Fig. 1), although similar levels of
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understanding exist for other mycotoxins (e.g. Kim et al. 2005; Alexander et al. 2009; Uhlig et al.
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2012; Niehaus et al. 2013). From the primary metabolite farnesyl diphosphate, 7-10 enzymatic
modifications lead to synthesis of trichothecene mycotoxins. Each enzymatic step in this
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process has been linked to a particular trichothecene biosynthetic (TRI) gene within or outside
of the primary TRI cluster (Fig. 1). The cluster includes additional genes that encode regulatory
proteins (TRI6, TRI10), a transporter (TRI12), and proteins of unknown functions (TRI9, TRI14)
(Kimura et al. 2007; Alexander et al. 2009).
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In some cases, chemotype variation results from differences in the presence and
absence of biosynthetic genes. For instance, TRI16 is responsible for addition of a five-carbon
moiety (isovalerate) to the oxygen at C-8 of the trichothecene molecule during biosynthesis of
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T-2 toxin (Fig. 1; Brown et al. 2003; Peplow et al. 2003). TRI16 is present and functional in
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species that produce T-2 toxin (e.g. F. sporotrichioides), but is absent or pseudogenized in
species (e.g. F. graminearum) that produce trichothecene variants like nivalenol (NIV) and
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deoxynivalenol (DON), which lack an isovalerate moiety (Fig. 1; McCormick et al. 2004;
Vanheule et al. 2016). Similarly, the presence or absence of a functional TRI13 gene is
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responsible for the DON and NIV chemotype polymorphism observed within F. graminearum
and related species (Fig. 1; Brown et al. 2002; Lee et al. 2002; Kimura et al. 2003), which has
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differences (Ward et al. 2002).
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been maintained by a form of balancing selection acting directly on these chemotype
In other cases, trichothecene chemotype variation results from differences in function
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of allelic variants of the same TRI gene. For instance, in most F. graminearum strains, TRI1 is
responsible for trichothecene oxygenation at both C-7 and C-8, leading to formation of variants
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like DON or NIV (Fig. 1; McCormick et al. 2004). However, in some F. graminearum strains, TRI1
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adds an hydroxyl group at C-7 only, which leads to formation of NX-2 and related toxins (Fig. 1;
Varga et al. 2015). In contrast, the F. sporotrichioides TRI1 adds an hydroxyl group at C-8 only,
leading to formation of T-2 toxin (Fig. 1; Brown et al. 2003; Meek et al. 2003). Similarly,
different TRI8 alleles are responsible for 3-acetyl-deoxynivalenol (3-ADON) vs. 15-acetyldeoxynivalenol (15-ADON) chemotypes in F. graminearum, depending on whether TRI8 deacetylates C-15 or C-3, respectively (Fig. 1; Alexander et al. 2011).
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As a result of this understanding that links genetic determinants with chemical
modifications to mycotoxin structure, the particular mycotoxin variant (i.e. chemotype)
produced by an unknown isolate or a novel species of Fusarium can be readily inferred using
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DNA-based methods. For instance, a multilocus genotyping assay was developed to
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simultaneously identify fusarium head blight pathogens and predict their trichothecene
chemotypes (Ward et al. 2008). Similarly, mycotoxigenic potential can be predicted by mining
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genome sequences for mycotoxin biosynthesis genes (Edwards et al. 2016; Gräfenhan et al.
2016). Chemotype predictions inferred from DNA-based analyses can be confirmed via chemical
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analysis of culture broths or extraction from solid culture substrates (Aoki et al. 2015; Edwards
et al. 2016; Gräfenhan et al. 2016), although actual production is not always observed in strains
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that have the necessary biosynthetic genes.
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Thus, prior investments to generate detailed understandings of the relationship
between genotype and chemotype facilitate rapid characterization of novel isolates and their
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toxigenic potential. It is also anticipated that this detailed mechanistic understanding of
mycotoxin biosynthesis will suggest targets for more effective prevention or control of
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mycotoxin contamination.
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Biotransformation of Fusarium mycotoxins
Biochemical modifications can substantially modulate the bioactivity of Fusarium
mycotoxins, and both plants and microbes belonging to disparate taxa have been described as
having the capacity for such enzymatic modifications (e.g. McCormick et al. 2012; He et al.
2015; Li et al. 2015). With sufficient understanding of these processes, there is the potential for
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practical, applied usage in mitigating economic losses due to mycotoxins. For instance,
enzymatic cleaning of contaminated grain may reduce mycotoxin content sufficiently to allow
for some uses of that grain. Alternately, enzymes that are able to reduce the toxicity of
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Fusarium pathogens, or improving the efficacy of biological control agents.
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Fusarium mycotoxins may represent novel strategies for enhancing plant defenses toward
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Several excellent reviews of microbial biotransformation of mycotoxins are available
(Palumbo et al. 2008; Awad et al. 2010; McCormick 2013; Vanhoutte et al. 2016). Screens for
mycotoxin-biotransforming microorganisms have led to the discovery of several different
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chemical transformations of DON and T-2 toxin. These include de-epoxidation (Fuchs et al.
2002), epimerization (Ikunaga et al. 2011), deacylation (Young et al. 2007), and glucosylation
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(McCormick et al. 2012).
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Trichothecene toxicity depends heavily upon the epoxide moiety of the molecule, and
opening the epoxide ring dramatically reduces toxicity (Zhou et al. 2008). Because oxygen
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status is linked to redox potential, and epoxide ring opening is a reductive process, it is not
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surprising that most reports of this biotransformation have involved anaerobic organisms and
culture conditions. Microbial strains or consortia displaying anaerobic DON de-epoxidation have
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originated from environments such as rumen fluid (Fuchs et al. 2002) and the digesta of catfish
(Guan et al. 2009) and chickens (Yu et al. 2010; Li et al. 2011).
The oxygen atom at the C-3 position is another portion of the trichothecene molecule
that imparts substantial toxicity. Acetylation of the C-3 oxygen helps protect Fusarium from the
toxic effects of the trichothecenes during biosynthesis (Kimura et al. 1998; McCormick et al.
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1999), but toxins are deacetylated in infected plant tissue, increasing their bioactivity. Addition
of glucose to the C-3 oxygen by plant glycosyltransferase enzymes can convert trichothecenes
into less toxic glycosides (Lemmens et al. 2005; Lin et al. 2008; Wetterhorn et al. 2016). For
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instance, expression of a barley glucosyltransferase in wheat enhances the resistance of the
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wheat to the secondary spread of F. graminearum through the spike (Li et al. 2015). Microbial
biotransformations at the C-3 position (formation of 3-epimer, 3-keto) have been reported
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from Gram-negative (Devosia sp.) and Gram-positive (Nocardioides sp.) bacteria (Ikunaga et al.
2011; Sato et al. 2012; He et al. 2015).
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Yeasts in the Blastobotrys (Trichomonascus) clade can also reduce toxicity of
trichothecenes by C-3 acetylation, C-3 glucosylation, and removing side groups from the
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trichothecene molecule (McCormick et al. 2012). From a food safety risk perspective, such
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biotransformations of mycotoxins pose challenges to detection if the structural change alters
the sensitivity of detection. For instance, an antibody test for the detection of T-2 toxin did not
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effectively detect the glucosylated form of the toxin (McCormick et al. 2015). This necessitated
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development of an antibody for glucosylated T-2 toxin (Maragos et al. 2013).
Additional screening for biotransformation may eventually lead to identification of
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enzymes that detoxify mycotoxins, which would be a boon for both plant protection and food
safety. However, it will be a challenge to design screening approaches that avoid re-discovering
already known biotransformations. It is not yet known whether the enzymatic machinery exists
for the mineralization of trichothecenes and other Fusarium mycotoxins. It is expected that
such metabolic capacity exists within soil microbial communities, as mycotoxins do not appear
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to accumulate in the environment. However, the description of the complete metabolism of
trichothecenes awaits further research.
Population biology of mycotoxigenic fusaria
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Analyses employing a combination of multilocus genotyping and neutral molecular
markers enable large-scale analyses of the diversity, mycotoxigenic potential, and population
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structure among fusaria (Gale et al. 2007; Ward et al. 2008; Gale et al. 2011; Bec et al. 2014;
Liang et al. 2014; Kelly et al. 2015; Liang et al. 2015). In North America, these studies have
revealed two dominant populations of F. graminearum, known as NA1 and NA2. These
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populations have distinct demographic histories; the NA1 population is genetically diverse and
comprised of native isolates that typically possess the 15-ADON chemotype, whereas NA2
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represents an invasive population that has undergone a bottleneck and is associated with the 3-
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ADON chemotype. The NA2 population has rapidly spread across major wheat growing regions,
and in recent decades, has become dominant in the Upper Midwestern US and in western and
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Maritime Canada (Liang et al. 2014; Kelly et al. 2015). However, such shifts have not occurred in
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eastern Canada and other parts of the US, where NA1 remains dominant (Schmale et al. 2011;
Bec et al. 2014; Kelly et al. 2015).
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Very recently, F. graminearum isolates possessing the novel NX-2 chemotype (see Fig. 1
for chemical structure), were found to be sympatric with NA1 and NA2 in southern Canada and
the northern US (Liang et al. 2015; Varga et al. 2015; Kelly et al. 2016). NX-2-producing F.
graminearum have undergone toxin diversification in response to changes in selection pressure
acting on the cytochrome P450 enzyme encoded by TRI1. This example demonstrates that
adaptive constraints on the molecular evolution of trichothecene genes may be population or
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niche-specific, and further indicates that mycotoxin chemotype differences may be important in
niche adaptation (Kelly et al. 2016).
While the ecological factors underlying F. graminearum population dynamics remain
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largely unknown, it would seem that a complex adaptive landscape of regional selection
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pressures has influenced the distribution of Fusarium head blight pathogen populations and
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mycotoxin chemotypes in North America. Such analyses of the population biology of
mycotoxigenic Fusarium spp. can inform assessment of the risks posed by introductions of
foreign pathogen genotypes, and can reveal geographic population structure, with implications
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for mycotoxin testing, fungicide resistance, and plant germplasm evaluation.
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Genomic analyses of secondary metabolite production
A rapidly increasing number of fully sequenced genomes has enabled comparative and
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functional genomics analyses aimed specifically at mycotoxins. Comparative genomic analysis
of secondary metabolite biosynthetic gene clusters in diverse genomes can identify chemotype-
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specific gene clusters (Semeiks et al. 2014) and novel metabolites (Wiemann et al. 2013), as
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well as providing insights into the evolution and origins of the genes responsible for secondary
metabolite biosynthesis (Sieber et al. 2014).
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There is wide variation in the presence and absence of mycotoxin biosynthetic genes
among Fusarium spp. (Brown and Proctor 2016). Increasingly, there is also evidence for intraspecies variation in gene content for mycotoxins or other secondary metabolites. For instance,
the biosynthetic gene cluster for fusarin production is intact in some strains of F. proliferatum,
while portions of the cluster, including critical genes for fusarin production, have been lost in
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other strains (Niehaus et al. 2016). Other taxa that have largely been considered nonmycotoxigenic have recently been shown to possess genes enabling the potential production of
diverse secondary metabolites; for instance, genomic analyses of F. avenaceum revealed 26
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polyketide synthase genes and 24 non-ribosomal peptide synthase genes, which likely confer
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the ability to produce the mycotoxins beauvericin/enniatins, fusarins and the fumonisin-like
metabolite 2-amino-14,16-dimethyloctadecan-3-ol (Uhlig et al. 2005; Lysøe et al. 2014; Hansen
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et al. 2015; Brown and Proctor 2016).
Diverse mechanisms have contributed to the distribution of mycotoxin biosynthetic
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genes, including vertical inheritance, gene loss, horizontal transfer, and gene duplication
(Proctor et al. 2009; Proctor et al. 2013; Niehaus et al. 2016). For instance, comparative
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genomic analyses have revealed a complex history of horizontal gene transfer and subsequent
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uneven degradation of the gene cluster responsible for the production of depudecin (Reynolds
et al. 2017), a histone deacetylase inhibitor produced by diverse Ascomycota. While some
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fusaria retain an intact and functional depudecin gene cluster, in others one or more depudecin
genes are non-functional (pseudogenized) or have been lost (deleted). Interestingly, two genes
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from the depudecin cluster tend to be preferentially retained; an efflux pump (DEP3), and a
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transcription factor gene (DEP6) that regulates DEP gene expression. This finding suggests that
retention of DEP3 and DEP6 provides a selective advantage, perhaps by conferring resistance to
exogenous depudecin or structurally similar metabolites (Reynolds et al. 2017).
Improved understanding of how biosynthetic gene cluster expression is regulated also
has the potential to improve management of mycotoxigenic fusaria, and can be informed by
genomic analyses. Most mycotoxin biosynthetic gene clusters include one or more genes
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coding for pathway-specific transcription factors, such as TRI6 and TRI10 in the trichothecene
biosynthetic cluster (Fig. 1), or FUB10 and FUB12 in the fusaric acid biosynthetic cluster (Brown
et al. 2014b). However, other clusters, such as the fusarin gene cluster, do not include a
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pathway-specific regulatory gene (Niehaus et al. 2013). Expression of genes in the latter
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clusters is likely controlled directly by global regulators encoded by genes located outside the
cluster (Brakhage 2013). In contrast, global regulatory elements likely exercise less direct
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control over clusters that encode a pathway-specific transcription factor(s) (Studt et al. 2012;
Niehaus et al. 2014), but more likely have indirect control via the transcription factor(s). These
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regulatory dynamics relate to the role of secondary metabolite production in the broader life
history strategy of fusaria that produce them. For instance, global regulatory elements may be
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required for broad reshaping of gene expression during transition from one habitat to another,
such as from saprotrophic growth to colonization of a living plant (Brown et al. 2014a).
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Finally, many secondary metabolite clusters of unknown function remain to be explored.
We anticipate that these metabolites play a role not only in plant-microbe interactions, but also
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in species interactions with other microbes.
Mycotoxigenic fusaria in a phytobiome context
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The success of Fusarium pathogens, and the accumulation of associated mycotoxins,
depends heavily on interactions with other organisms, and on environmental conditions. The
concept of the phytobiome has been recently championed as an integrating idea that ties
together plants, their environment, and the complex communities of organisms that interact
with plants (Young and Kinkel 2017). There remains much to understand regarding mycotoxin
production by fusaria from a phytobiome perspective. For instance, since fumonisins do not
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appear to be required for virulence in planta (Desjardins and Plattner 2000), do they instead
play a more active role in competitive interactions with other microbes?
Previous crop rotations, tilling practices, and other agronomic practices, which also
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influence soil microbial communities, have been shown to influence crop diseases and
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mycotoxin contamination caused by Fusarium. Additionally, weather is a key factor driving the
life-cycles of Fusarium and of other microorganisms within the phytobiome, and ultimately the
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host-pathogen interactions. Thus, to understand this complex ecological system, there must be
simultaneous consideration of the host plant, the pathogenic Fusarium, and the broader
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microbiome, all in relation to the abiotic environmental context.
Changes in climate directly influence host defense responses and therefore host-
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pathogen interactions. Several recent studies investigating the influence of climatic variables on
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host plant defenses against Fusarium infection and mycotoxin contamination have been
published (Vaughan et al. 2014; Vaughan et al. 2016a; Vaughan et al. 2016b). Corn grown at an
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elevated atmospheric carbon dioxide concentration ([CO2]) was more susceptible to F.
verticillioides proliferation, however it did not affect fumonisin contamination (Vaughan et al.
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2014). Changes to atmospheric [CO2] had cascading effects on plant gene expression that led to
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a compromised defense response on one hand, but a reduction in host plant factors that induce
mycotoxin production by F. verticillioides at the same time (Vaughan et al. 2014). However, the
combination of both elevated [CO2] and drought stress resulted in even greater susceptibility of
the plant to F. verticillioides proliferation and increased fumonisin contamination (Vaughan et
al. 2016b).
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While these results provide valuable information on direct host-pathogen interactions in
the context of different climatic variables, many other indirect effects of elevated [CO2] and
drought likely influence disease development and mycotoxin accumulation. For example,
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herbivore feeding damage is known to affect the susceptibility of host plants to Fusarium
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infection and mycotoxin contamination (Bowers et al. 2014). Weather variability also results in
changes in herbivore populations and feeding behaviors. Recent evidence suggests that
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elevated [CO2] also reduces the production and release of volatile organic chemical signals that
function in crop tri-trophic interactions (Block et al. 2017).
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The potential impacts of changing climate on the F. graminearum-wheat pathosystem
was recently reviewed (Vaughan et al. 2016a). Abiotic pressures influence the major processes
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of the saprotrophic and pathogenic phases of the fusarium head blight disease cycle, including
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inoculum production. Shifts in host plant phenology due to changes in dominant annual
weather patterns will also likely improve synchrony between pathogen inoculum production
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and host plant flowering, resulting in increases in disease development. Nevertheless, there
remains considerable uncertainty around the potential for altered environmental conditions to
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influence mycotoxin contamination, particularly since so many unknowns still exist regarding
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the direct and indirect impact of climate changes on the many ecological dynamics that can
influence host-pathogen interactions.
Recent research has used culture-independent techniques to semi-comprehensively
describe the complement of microorganisms associated with plants that host mycotoxigenic
fusaria (Karlsson et al. 2014; Nicolaisen et al. 2014; Grudzinska-Sterno et al. 2016; Hertz et al.
2016). These efforts have been complemented by culture-based efforts to collect isolates
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representative of the host plant microbiome (Yoshida et al. 2012; Comby et al. 2016). These
efforts are expected to advance the goal of effective biological control of mycotoxigenic fusaria
(Comby et al. 2017), whether through inoculation with antagonistic microbes or by means of
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managing the phytobiome to enhance pathogen suppression by the indigenous microbiome.
Conclusion
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Mycotoxigenic fusaria pose serious barriers to human well-being, animal health, and
agricultural productivity. However, transdisciplinary study of these fungi and their secondary
metabolites has produced powerful insights that will enable more effective control practices.
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Despite our growing understanding, it is clear that further research will continue to more
accurately define the food safety risks associated with mycotoxins produced by Fusarium spp.,
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and to illuminate the ecological factors that contribute to the success of these versatile and
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interesting organisms.
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Alexander NJ, McCormick SP, Waalwijk C, van der Lee T, Proctor RH. 2011. The genetic basis for 3-ADON
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Figure captions
Fig. 1 – Illustration of the biosynthetic pathway leading to production of trichothecenes, with
linkages shown to the corresponding gene cluster for three generically represented Fusarium
rip
Labels at the arrows indicate the TRI gene whose product enacts the indicated
t
species. (Chemotype, and corresponding genotype, differences can be found within species.)
biotransformation. DON = deoxynivalenol; 3-ADON = 3-acetyl-deoxynivalenol; 15-ADON = 15-
us
c
acetyl-deoxynivalenol; NIV = nivalenol; NX-2 = NX-2 toxin; T-2 = T-2 toxin. Colored polygons
indicate the presence and orientation of TRI genes within a genome. Gene lengths are not
an
drawn to scale. Discontinuities in the scaffold along which gene symbols are arranged indicate
distinct genetic loci. Ψ indicates a pseudogenized gene. Gene symbols are color-coded by
M
functional category, as indicated in the legend. The inset figure depicts a generic trichothecene
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backbone structure, and indicates the conventional numbering of atom positions.
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