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Article

Trichoderma harzianum in Biocontrol of Maize Fungal Diseases and Relevant Mycotoxins: From the Laboratory to the Field

1
Faculty of Technology Novi Sad, University of Novi Sad, Bulevar cara Lazara 1, 21000 Novi Sad, Serbia
2
Maize Research Institute Zemun Polje, Slobodana Bajića 1, 11185 Belgrade, Serbia
3
Institute of Field and Vegetable Crops, Maksima Gorkog 30, 21000 Novi Sad, Serbia
4
Patent Co., doo, Vlade Ćetkovića 1a, 24211 Mišićevo, Serbia
5
LoginEKO doo, Tiski red 117, 23207 Aradac, Serbia
*
Author to whom correspondence should be addressed.
J. Fungi 2025, 11(6), 416; https://doi.org/10.3390/jof11060416
Submission received: 28 April 2025 / Revised: 23 May 2025 / Accepted: 26 May 2025 / Published: 27 May 2025
(This article belongs to the Special Issue Plant Fungal Diseases and Crop Protection, 2nd Edition)

Abstract

Background: Maize, one of the world’s most important food and feed crops, is often threatened by fungal infections that not only reduce yields but also contaminate grains with harmful mycotoxins. Methods: This study evaluated the biocontrol potential of Trichoderma harzianum K179 as an eco-friendly alternative to synthetic fungicides for protecting maize from two major pathogens, Fusarium graminearum and Aspergillus flavus. T. harzianum K179 was cultivated in a lab-scale bioreactor, and its antifungal activity was assessed through in vitro inhibition assays and two-year field trials. During the field trial, maize ear disease severity, yield, and mycotoxin levels in maize samples were monitored to assess the efficacy of the produced Trichoderma biopreparation. Results: In laboratory tests, T. harzianum K179 significantly inhibited both target pathogens. Field trials demonstrated that seed treatments with the Trichoderma bioagent reduced ear rot severity and increased grain yield compared to untreated and chemically treated controls. Notably, maize samples from T. harzianum-treated plots contained lower concentrations of key mycotoxins, including fumonisins and aflatoxins. Conclusions: These findings highlight the usefulness of T. harzianum K179 in integrated pest management strategies, offering a sustainable solution that enhances crop safety and productivity while mitigating the environmental risks associated with chemical fungicides.

1. Introduction

As a final product of the plant life cycle, seed plays an important role in reproduction, survival, renewal of species, but also in the transmission of infection [1]. The seed of cultivated plants represents a suitable substrate for the development of microorganisms and pathogens, among which the most important place is occupied by fungi. Pathogenic microorganisms, primarily fungi that colonize maize seed can reduce grain yield and seed quality. Fungal infections in maize can lead to smaller kernel size, reduced protein content, and adverse effects on germination, resulting in lowered yield and feed quality [2]. Fusarium and Aspergillus species are among the most important causes of maize diseases. The most common Fusarium species detected on maize in Europe are F. graminearum and F. verticillioides [3,4,5,6]. Yield losses due to Fusarium ear rot on maize in Europe can range from 10% to 30% on average, but in severe cases, particularly under conditions of high infection, yield reductions can exceed 40% [7,8].
On the other hand, Aspergillus species, particularly Aspergillus flavus and A. parasiticus, are known to cause aflatoxicosis in maize and are predominant in warmer, tropical, and subtropical climates [9]. Recently, due to climate change their prevalence has shifted to temperate regions as well. Regions with warm, dry conditions favor the growth of Aspergillus species, making southern Europe particularly vulnerable, so that maize crops in countries like Spain, Italy, and southern France are often exposed to such conditions. However, the occurrence of Aspergillus infections has also been reported in other European regions, with the presence of A. flavus confirmed in Portugal, Western Romania, Serbia, Croatia, Slovenia, and Hungary [5,10,11]. Furthermore, the species A. parasiticus was isolated from maize seed for the first time in the growing season of 2012 in Serbia [12,13], while occurrence of A. niger and A. flavus on maize in Serbia was detected in the period 2008–2012 by Lević et al. (2013) [14]. On average, maize yield losses from Aspergillus infections in Europe range from 5% to 20%. However, in severe cases or during high-infection years, losses can be much higher, potentially exceeding 30% [15,16].
In addition to their pathogenicity, these species are known to have high toxicity potential due to the production of different secondary metabolites—mycotoxins [17]. The most important mycotoxins produced by Fusarium species are trichothecenes (T2, HT-2), zearalenone (ZEN), and fumonisins (FUM) [18]. On the other hand, aflatoxins are the most toxic secondary metabolites produced by A. flavus [19] and A. parasiticus [20], while ochratoxins are a group of mycotoxins produced mainly by A. ochraceus and A. carbonarius, but also by A. niger [21].
Produced mycotoxins reach an animal’s body through feed containing infected maize and lead to various negative changes. However, by consuming the meat, milk or eggs of infected animals, humans ingest mycotoxins that can cause various consequences in the human body [17]. F. graminearum is known to produce two significant toxins: trichothecenes deoxynivalenol (DON) and estrogenic ZEN. Acute DON intake is most often manifested by characteristic toxicological effects, such as reduced food intake and vomiting in animals [22]. Trichothecenes have a significant effect on protein synthesis and DNA and RNA synthesis which indicates the seriousness of their consumption [23]. On the other hand, ZEN affects the reproductive system in animals (hemorrhaging and atrophy of the ovaries) [22].
Another important Fusarium species, F. verticillioides, produces FUM, of which the most toxic is fumonisin B1 (FB1), which shows nephrotoxic and hepatotoxic effects on experimental animals [24]. This mycotoxin mainly causes abdominal pain and diarrhea in humans, but there is also information about the esophageal cancer [25]. The International Agency for Research on Cancer characterized FB1 as a group 2b possible carcinogen for humans [24]. Due to the harmful effects of FUM, The European Union (EU) established a recommendation of 1 µg FUM/kg body weight per day as the acceptable daily consumption for people [26].
According to the World Health Organization (WHO) several types of aflatoxins (AFs) occur in nature, but four aflatoxins, B1, B2, G1 and G2, are particularly dangerous to humans and animals. Large doses of aflatoxins lead to acute aflatoxicosis that can be life-threatening, causing liver damage. Chronic aflatoxin poisoning results in immunosuppressive and carcinogenic changes [27]. According to International agency for Research on Cancer aflatoxin B1 (AFB1) is classified in group 1a carcinogenic compounds for humans [28]. The highest standard level is set by the EU, where total AFs and AFB1 cannot exceed 4 µg/kg and 2 µg/kg, respectively [29].
Given that maize is a world-important agricultural crop used primarily in the diet of animals, adults, and babies as well, the presence of mycotoxins and fungal diseases in maize must be controlled. Climate change at the global level has proven to be the cause of numerous problems in the field and one of the leading ones is related to the appearance of mycotoxins in crops [30]. Due to the impossibility of controlling climate change, the application of fungicides has become the most common reliable solution for crop protection against pathogenic fungi and their dangerous toxins. However, the use of synthetic fungicides has led to another problem, which is their harmful effects on non-target organisms, human health, and the environment [31,32].
Because of all the above, scientists around the world have focused their research on finding more sustainable and eco-friendly ways for plant disease control and crop production. Therefore, the notion of biocontrol is closely linked to sustainable agricultural practices that are necessary to protect the environment and agricultural resources [32]. While fungicides have a temporary effect and mostly require reapplication, biocontrol agents have the ability to bind to the ecosystem in terms of reproduction and colonization of the rhizosphere. Fungi that belong to genus Trichoderma fully colonizes roots as they grow and provides at least season-long benefits to plants [33], producing antifungal compounds and enzymes that inhibit the growth of soil-borne pathogens, promoting plant health and thus reducing the need for chemical pesticides [34,35,36]. Trichoderma has proven to be very successful in biocontrol [32,37] inhibiting the growth of various phytopathogens [38,39], but also as a plant growth promoter of various crops—maize, wheat, soybean, lettuce, tomato, pepper, chilli, etc. [40,41,42,43,44]. The fact that Trichoderma species are resistant to most chemical pesticides makes those species good candidates for both, biocontrol and integrated control [35,45]. Worldwide distribution, fast growth and high spore production make those species easy to isolate, but not all Trichoderma strains are effective, so strain selection is of crucial importance.
Seed treatment is an effective strategy for controlling seed-borne diseases, with various methods available to suit different agricultural needs [46]. Due to the recognized need for seed treatment in the 20th century, specialized devices for seed treatment were developed with capacities that enabled their industrial application. These machines were developed for the purpose of applying preparations to seeds before sowing, thus contributing to the protection of agricultural crops from the beginning of their life cycle.
Accordingly, this study aimed to produce the Trichoderma harzianum K179 biocontrol agent in a lab-scale bioreactor and evaluate its antagonistic effect against major maize pathogens under in vitro and field conditions. Key parameters, including maize ear disease severity, yield, and mycotoxin levels in maize samples, were monitored to assess the efficacy of the produced Trichoderma biopreparation.

2. Materials and Methods

2.1. Fungal Material

All fungal strains used in the study were obtained from the Institute of Field and Vegetable Crops, Novi Sad (IFVCNS), Serbia, where they had been isolated according to the standard procedure of the IFVCNS Laboratory for Phytopathology, purified to single-spore strains according to Leslie and Summerell (2006) [47], identified and collected. All strains used in the study were stored on PDA slants in a refrigerator at 4 °C until use, with regular revitalization every 6 months.
T. harzianum strain K179 was obtained from soil sample collected at Belegiš, Vojvodina Province, Serbia. It was first identified according to its morphological characteristics following Samuels and Hebbar (2015) [48], which was confirmed by molecular identification through ITS1 and ITS2 regions, separated by the 5.8S ribosomal RNA gene (ITS, Internal Transcribed Spacer)—NCBI Acc. No. MN448464. A PCR assay for the translation elongation factor (TEF-1a) gene was conducted with primers TEF1-728 F and TEF1-986R, and the partial sequence obtained showed 99% identity with sequences of T. harzianum (KY236120.1; KY236119.1; KT357557.1) in the NCBI database and 99% identity with T. harzianum (ISTH-42GJS97-263) in the TrichoBlast ISTH database. T. harzianum K179 was used for in vitro and the field experiments, and inoculum preparation was performed according to Mitrović et al., 2023 [49]. Obtained inoculum was further used in a laboratory bioreactor experiment.
F. graminearum K28 and A. flavus K328 were isolated from infected maize seed grown at Rimski Šančevi, Vojvodina Province, Serbia. Morphological identification of single-spore strains K28 and K328 was achieved by following Leslie and Summerell (2006) [47] and Klich (2002) [50] identification manuals and by comparing macroscopic and microscopic characteristics of strains with the reference strain of F. graminearum sensu stricto (NRRL 5883), originating from maize in Ohio (USA), and the reference strain of A. flavus CBS 100927A, respectively. F. graminearum K28 and A. flavus K328 strains, as representatives of the most important maize pathogens, were used as test pathogens in vitro biocontrol study that was carried out according to Mitrović et al. (2023) [49].

2.2. Bioreactor Experiment

The experiment in a lab-scale bioreactor with a total volume of 3 L was carried out using an aeration intensity of 1.5 vvm and a stirring speed of 250 rpm as previously described in the study by Mitrović et al. (2023) [49]. The temperature was maintained constant at 28 °C during the bioprocess. The initial pH of the medium was about 6 before sterilization and was not adjusted afterwards. The bioprocess lasted until a cell concentration of 107 CFU/mL was reached. Appropriate electrodes and sensors, which are an integral part of the applied laboratory bioreactor equipped with the appropriate software package BioPAT® MFCS/win 3.1 (Biostat, Göttingen Germany), were used for bioprocess monitoring. The medium used for the cultivation of T. harzianum K179 had the following composition (g/L): dextrose (10), soybean flour (6.87), K2HPO4 (1.51), KCl (0.5) and MgSO4 × 7H2O (0.5). Before starting the bioprocess, 200 mL of the previously prepared T. harzianum K179 inoculum was added to 2 L of medium for cultivation.
Cultivation broth was sampled every 3 h of bioprocess in order to monitor the concentration of multiplied T. harzianum K179 cells by using an automated cell counter (Countess, ThermoFisher, Waltham, MA, USA). The bioprocess was stopped when the result of three simultaneous measurements showed a cell concentration of 107 CFU/mL.

2.3. In Vitro Experiment

For the in vitro experiment, 10 mL of the produced cultivation broth was set aside in order to confirm its biocontrol/antagonistic activity against phytopathogens. The rest of the cultivation broth was used for further field experiments. In vitro biocontrol test of the produced T. harzianum K179 bioagent was performed in Ø 90 mm Petri dishes. As representative phytopathogens, F. graminearum K28 and A. flavus K328 strains were used. The test was performed by well diffusion method described by Grahovac et al. (2020) [51]. The second layer, consisting of 1.2% PDA and pathogen, was applied to the first layer of pure PDA medium. The pathogen was previously prepared in PDB medium, filtered through a double layer of sterile gauze, and added to the previously prepared 1.2% PDA medium at a concentration of 35%. After solidification of the abovementioned media, 100 μL of the tested T. harzianum 179 cultivation broth was added to the prepared wells. After 7 days of incubation at 27 °C, the diameters of inhibition zones formed against phytopathogenic strains were measured. The in vitro biocontrol experiment was performed in triplicate.

2.4. The Field Trial

The field experiment was carried out at the site Rimski Šančevi (45° 46′ north latitude and 19° 20′ east longitude, Novi Sad, Serbia) during the 2021 and 2022 growing seasons (May–October) according to the standard protocol. The field where the experiment was conducted, is located in the northern part of Serbia, an area with a semi-arid continental climate. Data on climate conditions during the analyzed seasons are publicly available at the Republic Hydrometeorological Service of Serbia and in the Supplementary Materials. Commercial hybrid NS2662 intended for animal and human consumption was used in the study. In order to avoid artificial inoculation with phytopathogens in the field, maize seeds that were naturally infected with Aspergillus and Fusarium pathogens were selected and used for a field experiment. Preliminary analysis of seed fungal infection according to the ISTA procedure was done by Accredited Laboratory for seed testing within the IFVCNS. The results showed that seed of hybrid NS2662 intended for the field test was infected with fungi from the genera Aspergillus spp. (2%) and Fusarium spp. (4%).
The field experiments were set up as a split-plot design including four treatments and a control, all distributed in four blocks. The experimental plot area per treatment was 19.5 m2. The plot included four rows, each measuring 6.5 m, with 0.75 m between rows and 0.2 m between plants in row. Standard cultivation practices were applied according to the local agroecological conditions.
Produced T. harzianum K179 cultivation broth used for the field experiment contained 107 CFU/mL (Countess, ThermoFisher). Seed treatments before sowing were as follows: T1—control (untreated seed); T2—synthetic fungicide (25 g/L fludioxonil + 10 g/L metalaxyl-m); T3—T. harzianum K179 cultivation broth applied using a seed-coating machine; T4—T. harzianum K179 cultivation broth applied using a seed-coating machine with the addition of glue; and T5—immersion in T. harzianum K179 cultivation broth for 1 h. Figure 1a,b shows the method of seed treatment before sowing and the sowing procedure (Figure 1c).
The field bioefficiency parameters that were measured/monitored were disease severity and grain yield.
Disease severity was determined on each tested maize ear using a 7-point scale in relation to ear infection, where 1 = 0% infection; 2 = 1–3% infection; 3 = 4–10% infection; 4 = 11–25% infection; 5 = 26–50% infection; 6 = 51–75% infection; and 7 = 76–100% infection [52]. Twenty maize ears harvested sequentially from the side rows of each experimental plot were used for evaluation.
Grain yield was estimated after harvest. The two middle rows of each experimental plot were used to estimate the grain yield [53]. The experiment was sown and harvested by machines. At harvest, grain weight and moisture content were recorded for each experimental plot. Grain yield (t/ha at 14% moisture) was determined by the following formula:
weight of sample (kg) × (100 − moisture content %)/86 × (10,000/plot area)

2.5. Mycotoxins Detection

Both side rows of each treatment were harvested, and the collected maize kernels were adequately homogenized. After homogenization, maize kernels of each applied treatment in four repetitions were delivered in standard bags for mycotoxins detection. The delivered samples were passed through a separator and 500 g of a representative sample was used for analysis. Kernel mycotoxin analysis was conducted for two spontaneously selected repetitions of the same treatment.
RETSCH ZM200 mill was used to homogenize the samples. Following the manufacturer’s recommendations, the mill was cleaned after each sample to prevent sample cross-contamination. Sample extraction was performed using 20 mL of extraction solution (acetonitrile:water:formic acid = 79:20:1). Samples were further placed on a horizontal shaker (MAXQ 4450, ThermoScientific) for 90 min (250 rpm). After 90 min, the samples were centrifuged (Eppendorf centrifuge 5804) for 5 min at 4500 rpm. The extracts were diluted with ultra-pure water (<0.055 µS/cm). Before analysis, the liquid samples were passed through a nylon filter (0.22 µm; AMTAST, Lakeland, FL, USA, p/n: SFNY013022NA).
The analysis was performed on an LC-MS/MS Agilent Technologies (Santa Clara, CA, USA) device equipped with the following: Agilent ZORBAX Rapid Resolution HT 4.6*50 mm 1.8 µm column, ZORBAX Eclipse Plus C18, 2.1 mm, 1.8 µm, UHPLC guard column, autosampler Agilent Technologies 1290 series II with thermostat and column oven, Agilent Technologies 1290 series II Flex pump and MS/MS detector Agilent Technologies 6460c MS/MS QQQ with Jet Stream electrospray ion source. The mass spectrometer analyses were carried out using selected reaction monitoring channels in positive electrospray ionization (ESI+) mode.
Maize samples were analyzed to determine the potential presence of the following mycotoxins: aflatoxin B1 (AB1), aflatoxin B2 (AB2), aflatoxin G1 (AG1), aflatoxin G2 (AG2), deoxynivalenol (DON), fumonisin B1 (FB1), fumonisin B2 (FB2), T-2, HT-2, ochratoxin A (OTA), and zearalenone (ZEN).
Quantification of mycotoxins by LC-MS/MS was achieved by adding internal standards for each group of mycotoxins [13C17] aflatoxin B1; [13C15] deoxynivalenol; [13C18] zearalenone; [13C20] ochratoxin A; [13C34] aumonisin B1; [13C24]; T-2.

2.6. Data Analysis

The obtained values of inhibition zone diameters in the in vitro biocontrol experiment were processed in the program Statistica.Ink 13.0, using One-way ANOVA.
Grain yield was analyzed using a linear mixed-effects model with the following formulation (1):
y = μ + b l k + t r t + ε
where y is the grain yield; μ is the overall mean; blk is the random effect of block with b l k ~ N ( 0 , σ _ b l k ^ 2 ) ; trt is the fixed effect of the treatment; ε is the random residual effect, with ε ~ N ( 0 , σ _ ε ^ 2 ) . Two linear models with the same formulation were fitted on a per-year basis. The means of treatments were compared with a Tukey multiple comparison test. The results were graphically presented as means of treatment with their corresponding standard error of difference, providing a clear depiction of treatment differences.
The proportional odds model (POM) is a type of ordinal regression used to analyze outcomes that are naturally ordered-in this case, the disease severity ratings caused by phytopathogenic fungi. In our two-year experiment evaluating five biological treatments, the disease severity was assessed on an ordinal scale, and the POM was estimated separately for each year. In this model, instead of modeling the probability of each individual category directly, we model the cumulative probabilities (π). Specifically, if Y is the ordinal response variable with categories 0, 1, …, J, the model considers the cumulative probability γ j = P ( Y j ) or each cut-point j. These cumulative probabilities are linked to the predictors (e.g., the type of biological treatment) using the logistic function (2):
l o g i t ( γ j ) = l o g ( γ j / ( 1 γ j ) ) = θ j β
where θj represents the threshold (or cut point) for ordinal category j, β is the coefficient determining the effect of the biological treatments, and X denotes the independent variable (i.e., the treatment effect) in the POM. Additionally, the model is referenced to the control treatment, so that the estimated coefficients for the other treatments reflect their deviation from this reference, enabling direct comparisons of treatment effects. A key assumption of the POM is that the effect of the predictors (as captured by β) remains constant across the different cumulative logits. This is known as the proportional odds assumption, which implies that the odds ratio between any two adjacent categories is the same regardless of where the threshold is set [54].
Parameters in this model are typically estimated using maximum likelihood methods, and the significance of treatment effects is assessed. By modeling the cumulative probabilities, the POM provides an adequate framework to evaluate how different treatments shift the overall distribution of disease severity. The POM accommodates the ordinal nature of the disease severity ratings and allows for a direct comparison of the efficacy of the five biological treatments across the two separate experimental years.

3. Results

3.1. In Vitro Biocontrol Experiment

In order to test the efficiency of the produced T. harzianum K179 cultivation broth against isolates of F. graminearum K28 and A. flavus K328, the in vitro biocontrol experiment was performed. The results of the obtained inhibition zone diameters are shown in Figure 2.
The results show that the maximum mean diameters against both tested pathogens were formed after 36 h of T. harzianum 179 cultivation in the bioreactor. From Figure 2, it can be concluded that the pathogenic maize isolate, F. graminearum K28 was more sensitive to the produced T. harzianum K179 cultivation broth compared to isolate A. flavus K328. Maximum obtained mean diameter of the zone formed against isolate F. graminearum K28 was 57.67 mm, while the maximum mean diameter formed against isolate A. flavus K328 was 36.67 mm. Certainly, based on the obtained results, it can be concluded that the produced T. harzianum 179 cultivation broth shows extremely good antifungal activity in vitro against the tested maize phytopathogens. This result served as the basis for further testing of T. harzianum 179 cultivation broth under in vivo conditions in the field.

3.2. Field Experiment

3.2.1. Disease Severity

The effectiveness of the applied treatments was estimated using the disease severity scale and the appropriate regression model, proportional odds model, for ordered categorical data. The results of the study showed that there was a statistically significant difference between the applied treatments at the significance level of p < 0.01 in terms of disease severity.
The results presented in Table 1 show that treatments T3, T4, and T5 (treatments with the applied T. harzianum K179 bioagent) showed statistically very significant differences compared to control (p < 0.01), while treatment with synthetic fungicide T2, showed marginally significant differences compared to control (p < 0.05) in 2021 season. This is in accordance with results from field experiments conducted by Sangeetha (2009) [55] and Degani and Dor (2021) [56].
In order to analyze the obtained data using disease severity scale and in accordance with the applied model, the cumulative probability is presented in Figure 3. The severity of the disease was determined by grades from 1 to 7, while cumulative probabilities, π1–π6, were calculated accordingly. The probabilities for categories 5, 6, and 7 will be considered in more detail, as they indicate the highest severity of the disease and consequently the potentially highest yield loss [54].
Analysis of individual treatments shows differences in the probability of disease severity. During season 2021, the control treatment, T1 (Figure 3), had the highest estimated probability for grades 3 (0.442) and 4 (0.390), while, for the other grades, the cumulative probability was less than 0.1. The lowest probability for the T1 treatment was recorded for grade 1 (0.001), indicating the presence of a very small number of completely healthy maize ears. A similar cumulative probability was observed for the synthetic fungicide treatment T2. Namely, the highest estimated probability was registered for grade 3 (0.566), significantly lower probability for grade 4 (0.243) and 2 (0.144), while other disease severities had probabilities with values less than 0.1.
From Figure 3, it can be seen that for treatments T3, T4, and T5 the dominant cumulative probability was for grade 2. This indicates that by applying these treatments, the largest number of tested samples were almost healthy. Treatments T4 and T5 had the same cumulative probability value of 0.808 which was higher compared to treatment T3 (0.738). Also, all treatments with the applied T. harzianum K179 biocontrol agent (T3–T5) had a cumulative probability 0 for grade 6, while for T4 treatment cumulative probability 0 was also present for grade 5. This indicates that treatment with the applied T. harzianum K179 had no maize ears rated with scale 7. Compared to the other treatments, the T4 treatment also had the highest estimated probability for grade 1 (0.133) indicating that in the trial conducted during the 2021 season, the T4 treatment provided the highest number of completely healthy maize ears.
In general, compared with the results of the control treatment (T1), it can be concluded that the highest estimated probabilities for grades 1 and 2 were observed in treatments T4 and T5, i.e., treatments in which the T. harzianum K179 biocontrol agent was used. Therefore, in those treatments, the highest percentage of healthy maize ears was registered. The reason for this result was probably the fact that, in these treatments, T. harzianum K179 better colonizes the root of the plant and leads to the induced systemic resistance of the plant against pathogenic fungi [57].
It can be assumed that the difference between treatments T3 and T4, in which the T. harzianum K179 cultivation broth was applied using a seed-coating machine, was due to the application of glue in the treatment T4. On the other hand, both treatments T4 and T5 showed good antifungal activity. Specifically, in treatment T4, the glue enabled better fixation of the biocontrol agent T. harzianum K179 to the seeds, while in treatment T5, the seed immersion in T. harzianum K179 broth for 1 h enabled partial soaking of the seeds and thus better adhesion of T. harzianum K179 to the seed.
Further, Table 2 shows the results of the field trial conducted during 2022 at the same location and using the same experimental design. Observing the results obtained during the 2022 growing season (Table 2), it can be noticed that there was a statistically very significant difference (p < 0.01) between the control treatment T1 and treatments T3, T4 and T5. In contrast to the previous year (Table 1), in the field experiment conducted in 2022, the treatment with the synthetic fungicide (T2) was not statistically significant in relation to the control treatment. Thus, the results indicate the great potential of T. harzianum K179 as a biocontrol agent for the most common maize pathogens.
In order to analyze the obtained data for disease severity in accordance with the applied model, the cumulative probability for the 2022 season is presented in Figure 4. The severity of the disease was determined by grades from 1 to 7, while cumulative probabilities, π1–π7, were calculated accordingly.
From Figure 4, it can be observed that treatments T4 and T5 had the highest estimated probability for grade 1. This indicates that these treatments produced the healthiest maize ears, with no visible disease symptoms. Additionally, both treatments showed a cumulative probability of zero for categories 6 and 7 on the ordinal disease severity scale, indicating that no ears exhibited infection levels above 51%.
The T3 treatment also showed statistically significant differences compared to the control treatment. In the T3 treatment, the highest cumulative probability was for category 2, suggesting that this treatment also has as a biological control treatment.
On the other hand, no statistically significant difference was observed between the treatments T1 and T2 (Table 2). Both treatments had the highest value of cumulative probability for grade 4, indicating that most maize ears exhibited severe signs of infection. At the same time, the lowest values of cumulative probability were recorded for grade 1, indicating that the least number of completely healthy maize ears was recorded in treatments T1 and T2 (Figure 4).

3.2.2. Grain Yield

Grain yield is a key indicator of the effectiveness of seed treatments on crop production success. Figure 5 presents maize yield results during the 2021 and 2022 growing seasons. From Figure 5, it can be concluded that there were significant differences in yield between the two growing seasons. It is obvious that the influence of climatic conditions, which mostly vary from year to year, can contribute to an increase/decrease in yield. In addition to external influences, certainly, the influence of crop genotype also plays a significant role [58].
If the results for the two seasons are compared, it can be concluded that the yield is higher in 2021 compared to the 2022 growing season. The reason for this could be the aforementioned climatic conditions, which in 2021 were more favorable for maize cultivation. On the other hand, if we compare the effect of the treatment on the yield, it can be registered that there are significant statistical differences between treatments. Therefore, in both seasons, the control was at the same level of statistical significance (marked with a lowercase letter a) as the treatment T2—synthetic fungicide, while the treatments with the applied T. harzianum K179 showed a significantly better yield compared to the control.
During the 2021 season, it was observed that the treatments T2, T3, T4, and T5 are also at the same level of statistical significance (indicated by a lowercase letter b) in terms of grain yield. However, considering the less favorable season for maize cultivation, the 2022 season, the conclusion is different. Namely, treatments T4 and T5 (indicated with a lowercase letter c), i.e., treatments containing T. harzianum K179, were at the highest level of statistical significance compared to control and synthetic fungicide. Therefore, treatments with applied T. harzianum K179 showed better grain yield compared to the control T1, but at the same time compared to the treatment T2 with a synthetic fungicide.

3.3. Mycotoxins

In order to obtain all the necessary information about the impact of different treatments during two different growing seasons, an analysis of the presence of mycotoxins in maize was performed. Table 3 contains the results obtained from the analysis of maize samples collected in October 2021. The results showed that in all samples, regardless of the applied treatment, the presence of aflatoxin, ochratoxin A, ZEN, and DON was not found. The reason for this may be the influence of favorable climatic factors during the 2021 season, which was favorable for maize cultivation [59] and at the same time unfavorable for the development of fungal infections [60].
In addition to the above, the presence of fumonisins B1 and B2, as well as the trichothecene mycotoxins T-2 and HT-2, was detected in the samples. Analyzing the detected amounts of FB1 and FB2, differences between the applied treatments were observed. Namely, the analysis of the results shows that high amounts of FB1 and FB2 were detected in the control treatment and the synthetic fungicide treatment (T1 and T2), respectively. Significantly lower amounts of these two mycotoxins are detected in the T3 and T4 treatments, in which T. harzianum 179 was applied, while the lowest amount was detected in the T5 treatment. This was expected given that Yates et al. (1999) [61] and Rojo et al. (2007) [62] confirmed that Trichoderma suppresses the production of FB1.
However, an interesting result emerged in the detection of trichothecene mycotoxins. Namely, a significant amount of T-2 and HT-2 was detected in one of the samples treated with a synthetic fungicide (T2), while in all other samples these mycotoxins were not detected. Therefore, according to the obtained results, it can be concluded that the 2021 growing season was more favorable for the development of Fusarium than for Aspergillus species.
The results of mycotoxin analysis in samples from the 2022 growing season are shown in Table 4. The results of aflatoxin analysis show that the control samples (T1) contained significant amounts of aflatoxins B1 and B2, while the presence of these two mycotoxins was also observed in the synthetic fungicide treatment (T2) in slightly smaller amounts compared to the control. At the same time, aflatoxins G1 and G2 were not detected in samples. In contrast to these treatments, no aflatoxins were detected in the T. harzianum K179 treatments (T3, T4, and T5). Also, ochratoxin A was not found in any of the analyzed samples. These results are in accordance with the results of Ren et al. (2022) [63] and Dini et al. (2022) [64] who confirmed the positive effect of Trichoderma isolates in suppressing the production of aflatoxins and ochratoxin A.
By observing the detected amounts of ZEN and DON, it can be concluded that the presence of ZEN was observed only in the analyzed control samples. On the other hand, as in the previous 2021 season, the presence of FUM was observed in all tested samples. Also, the detected amounts of FUM are significantly higher than in the previous season. Analyzing the results, it can be noticed that during the 2022 season, the lowest FUM concentrations were observed in treatments T4 and T5. This is in accordance with the results shown in Figure 4, from which it can be noted that the treatments T4 and T5 had the highest number of healthy corn ears. Mycotoxins T-2 and HT-2 were not detected in any sample during the 2022 growing season.
Climate change, such as rising temperatures and changing rainfall patterns, has been found to be a key cause of fungal growth and crop contamination [65]. Considering that 2022 was a dry year compared to 2021, which was favorable for the multiplication of Aspergillus species [60], it was expected that aflatoxins would be present in the samples collected during the 2022 growing season. At the same time, the results showed that the use of T. harzianum K179 in biocontrol has great potential for suppressing aflatoxin-producing Aspergillus species.

4. Discussion

The results obtained in the in vitro biocontrol experiment shows a large difference in the sensitivity of two maize phytopathogens, F. graminearum K28 and A. flavus K328; however, it is considered that all diameters larger than 22 mm indicate that the applied agent is highly effective [66]. Thus, it can be concluded that the inhibition zone diameters obtained in the in vitro biocontrol experiment are significantly larger than the abovementioned value, and that T. harzianum K179 cultivation broth produced in the bioreactor under defined conditions can be used for the field experiment. These results match those of our previous research [49] and enabled us to conduct a complex trial in the field. Certainly, these results were expected given that the exceptional antifungal activity of T. harzianum against A. flavus was confirmed by Chiuraise et al. (2015) [67] and Kifle et al. (2017) [68] in their studies. Tian et al. (2018) [69], on the other hand, concluded in their study that three tested Trichoderma isolates, including the species T. harzianum, were proven to be potential candidates for control of F. graminearum ZEN producers.
By comparing the results obtained during the field trials carried out in 2021 and 2022 seasons, the certain differences were registered. Beneficial soil microbes, particularly those from the genus Trichoderma, are tested as viable and sustainable resources for promoting plant growth and alleviating biotic and abiotic stressors in research and commercial production environments [70]. Certainly, by analyzing the disease severity results, it can be concluded that during both growing seasons, the results showed exceptional efficacy of T. harzianum in controlling fungal infections of maize in the field. This is not surprising since the very successful seed treatment with T. harzianum on groundnut in controlling A. flavus and aflatoxins was confirmed by Chiuraise et al. (2015) [67]. Similarly, Saravanakumar et al. (2017) [71] in their study confirmed the exceptional potential of T. harzianum in controlling F. graminearum on maize. Results obtained in this research showed that it was necessary to either extend the treatment time or add an adjuvant (glue) in order to ensure that T. harzianum binds better to the seed and thus better exhibits its antifungal activity. Certainly, in addition to the pronounced impact on biotic stress and the significant use of Trichoderma spp. in biocontrol, this genus shows a remarkable impact on abiotic stress [72].
Based on Republic Hydrometeorological Service of Serbia (RHMS) [73] data on minimum and maximum temperatures and precipitation, it can be noticed that the 2022 season was extremely dry compared to the 2021 season. The significant differences in maize grain yield observed between the two studied years are probably the result of climatic factors, precipitation and air temperature, which are the most influential elements affecting maize cultivation in an observed region. Specifically, in 2022, when significantly lower grain yield was recorded, the observed site experienced the hottest summer since the beginning of meteorological measurements in 1951 (Seasonal Bulletin for Serbia, Republic Hydrometeorological Institute, 2022) [73]. In addition to extreme temperatures during the flowering and pollination phases, July—the most critical period for maize in terms of water needs, was characterized by only 13.8 mm of precipitation, which is almost ten times less than the maize water needs for that month. The combination of these unfavorable conditions led to the occurrence of extreme drought, which significantly reduced maize yields in the wider growing region. In contrast, in July 2021, the same site received 114.4 mm of precipitation, which proved to be a decisive factor contributing to the significant differences in yields between the two observed years (Supplementary Materials). Considering that climate change is a significant barrier to sustainable agricultural output in the twenty-first century, it can be assumed that probably the influence of abiotic stress is responsible for this difference. It is well known that alterations in precipitation patterns, carbon dioxide concentrations, temperature and the frequency and intensity of extreme events such as flooding, drought and hail significantly impede the attainment of food security for the growing population [74].
Given that the 2021 and 2022 seasons were completely different in terms of climatic conditions, we can conclude that the differences we obtained in this research for grain yield were expected. A variety of factors, including crop, genotype of the plant, biocontrol agent application method (soil, root and seed), delivery mechanism, inoculum concentration and environmental and soil conditions, might affect a plant’s reaction to Trichoderma spp. treatment. Our study provides valuable insights into how these different factors interact with Trichoderma, and our findings can guide future studies and practical applications by identifying the conditions under which Trichoderma is the most effective. Moreover, understanding how Trichoderma behaves under various conditions is crucial for optimizing its use in agriculture. Water deficiency stress triggers physiological reactions in plants, including reduced photosynthesis, stomatal closure, decreased cell development and increased respiration. Plants inoculated with Trichoderma improve water-deficit tolerance by regulating drought-induced changes in stomatal opening, enhancing root development, chlorophyll content in leaves and photosynthesis. Thus, using biological agents, such as water deficit-tolerant Trichoderma, could be a cost-effective, environmentally benign and long-term strategy for reducing drought stress [70].
Chepsergon et al. (2012) [75] verified the favorable influence of T. hamatum on the cocoa plant and T. harzianum T22 on tomatoes during drought. Also, Scudeletti et al. (2021) [76] tested T. asperellum’s impact on sugarcane during a drought. They found that the plant’s physiological characteristics, such as photosynthetic pigments, stomatal conductance, water use efficiency, and antioxidant metabolism, are all impacted by the microorganism’s inoculation. All of these elements contributed to plant growth and a high yield despite the drought. T. harzianum isolates PB23 and PB9 were also found to have a favorable effect on Brassica juncea plants under drought circumstances [77]. Cornejo-Ríos et al. (2021) [78] found that tomato plants primed with T. asperellum reduced physiological and agronomic symptoms associated with drought and chilling stress, and through improved antioxidant regulation and T. koningii showed helped provide tomato plants resistance to heat stress. When applied under high-temperature stress, this strain decreased the production of ROS (reactive oxygen species) and shielded the plant cells from oxidative damage [79].
The presence or absence of mycotoxins can be related to climatic conditions, but also to the presence/absence of adequate agents to control the fungi that produce them. During the 2021 growing season, it can be concluded that there were no detected mycotoxins produced by Aspergillus species. Given that warm, dry conditions favor the growth of Aspergillus species, it can be concluded that the 2021 season was probably not conducive to the growth of Aspergillus species and thus the production of aflatoxins and ochratoxin A [5,10]. What can also be noted is that the mycotoxins produced by F. graminarum, DON and ZEN, were also not detected during the 2021 season. On the other hand, presence of FB1 and FB2 proves that the maize was infected mainly by F. verticillioides or other Fusarium species from Liseola section. However, the amounts of these mycotoxins varied significantly among the applied treatments. Thus, the highest amount of detected fumonisins was present in the control sample, T1, while the lowest amount of FUM was present in treatments T4 and T5. These differences were expected given that Ferrigo et al. (2014) [57] confirmed that T. harzianum T22 induces in maize systemic resistance against F. verticillioides. Subsequently, Jambhulkar et al. (2022) [80] determined that T. harzianum BThr29 has the potential to be used in the control of F. verticillioides causing post flowering stalk rot in maize. Interestingly, T-2 and HT-2 were detected only in one sample treated with a synthetic fungicide.
During the 2022 growing season, the situation was different compared to the previous season. Namely, during this season, the presence of aflatoxins produced by Aspergillus species was detected in some samples. This was expected given that climatic conditions during the 2022 growing season were fully conducive to the growth of Aspergillus species. The results show that aflatoxins were detected in the T1 treatment in the highest amounts, as well as in the T2 treatment in a slightly smaller amount. However, it is interesting that aflatoxins were not detected in the treatments with the T. harzianum 179 cultivation broth. Considering that Chiuraise et al. (2015) [67], Kifle et al. (2017) [68] and Ren et al. (2022) [63] have demonstrated the very good antagonistic activity of Trichoderma isolates, especially T. harzianum, in the biocontrol of Aspergillus species, it can be concluded that the results obtained in this study were expected. Another difference compared to the 2021 growing season is the presence of ZEN mycotoxins in the control sample, which is an indicator of the presence of infection with the fungal species F. graminearum. However, Tian et al. (2018) [69] determined the antagonistic potential of Trichoderma spp. in the control of ZEN and F. graminearum. During the 2022 season, aflatoxins G1 and G2, ochratoxin A, DON, T-2, and HT-2 were not detected in the analyzed samples. However, as in the 2021 season, the presence of fumonisins B1 and B2 was registered in all samples during the 2022 season, but in significantly higher quantities.
So, by comparing the results for disease severity and the presence of mycotoxins, we can draw several conclusions. Notably, since the 2022 season was more favorable for fungal development and mycotoxin production (Table 4), the presence of mycotoxins was significantly higher compared to the 2021 season (Table 3). However, it is evident that all treatments involving T. harzianum 179 resulted in either the absence or a reduction of mycotoxin levels compared to the control treatment, and even compared to the synthetic fungicide treatment. At the same time, disease severity results for the 2022 season indicate that treatments T3–T5 were the most effective (Figure 4). Therefore, we can conclude that in the extreme conditions of 2022, T. harzianum 179 demonstrated strong biocontrol potential while also helping to mitigate the negative effects of abiotic stress. These findings further confirm the significant potential of the Trichoderma genus in alleviating both biotic and abiotic stress in plants [72].

5. Conclusions

This study shows the potential of sustainable solutions to some of agriculture’s biggest challenges. The fungus T. harzianum K179 proved to be an effective natural alternative to chemical fungicides for protecting maize from harmful fungal diseases and reducing toxic mycotoxin contamination. In field trials, seeds treated with this bioagent produced healthier plants, suffered less from disease, and had higher yields, even in seasons with challenging weather conditions. What is more, maize from treated plants contained significantly lower levels of harmful substances like aflatoxins and fumonisins, which are dangerous to both animals and humans. These results suggest that T. harzianum K179 not only enables better crop performance but also helps produce safer food and feed. This research paves the way for broader use of biocontrol agents in modern agriculture.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/jof11060416/s1.

Author Contributions

Conceptualization, I.M. and B.M.; formal analysis, M.Z.; investigation, I.M., P.Č. and S.Ć.; methodology, P.Č. and H.F.; resources, S.T.Ž. and M.V.; supervision, M.V.; validation, H.F. and B.M.; visualization, M.Z. and B.M.; writing—original draft preparation, I.M. and P.Č.; writing—review and editing, S.T.Ž. and S.Ć.; All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by the Ministry of Science, Technological Development, and Innovation of the Republic of Serbia (project Nos. 451-03-136/2025-03/200134; 451-03-136/2025-03/200040; and 451-03-136/2025-03/200032).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The original contributions presented in the study are included in the article and Supplementary Materials. Further inquiries can be directed to the corresponding author.

Conflicts of Interest

Authors Hunor Farkaš, Marko Vasiljević, Svetlana Ćujić were employed by the company Patent Co., doo. Author Miroslav Zorić was employed by the company LoginEKO doo. The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

References

  1. Shahzad, R.; Khan, A.L.; Bilal, S.; Asaf, S.; Lee, I.-J. What Is There in Seeds? Vertically Transmitted Endophytic Resources for Sustainable Improvement in Plant Growth. Front. Plant Sci. 2018, 9, 24. [Google Scholar] [CrossRef] [PubMed]
  2. Suleiman, R.A.; Rosentrater, K.A.; Bern, C.J. Effects of deterioration parameters on storage of maize. In Proceedings of the Agricultural and Biological Engineers, Kansas City, MO, USA, 21–24 July 2013; p. 1. [Google Scholar]
  3. Logrieco, A.; Mule, G.; Moretti, A.; Bottalico, A. Toxigenic Fusarium species and mycotoxins associated with maize ear rot in Europe. Eur. J. Plant Pathol. 2002, 108, 597–609. [Google Scholar] [CrossRef]
  4. Thompson, M.E.; Raizada, M.N. Fungal pathogens of maize gaining free passage along the silk road. Pathogens 2018, 7, 81. [Google Scholar] [CrossRef] [PubMed]
  5. Szabo, B.; Toth, B.; Toth Toldine, E.; Varga, M.; Kovacs, N.; Varga, J.; Kocsube, S.; Palagyi, A.; Bagi, F.; Budakov, D.; et al. A New Concept to Secure Food Safety Standards against Fusarium Species and Aspergillus flavus and Their Toxins in Maize. Toxins 2018, 10, 372. [Google Scholar] [CrossRef]
  6. Masiello, M.; Somma, S.; Ghionna, V.; Logrieco, A.F.; Moretti, A. In Vitro and in Field Response of Different Fungicides against Aspergillus flavus and Fusarium Species Causing Ear Rot Disease of Maize. Toxins 2019, 11, 11. [Google Scholar] [CrossRef]
  7. Xu, Y.; Zhang, Z.; Lu, P.; Li, R.; Ma, P.; Wu, J.; Li, T.; Zhang, H. Increasing Fusarium verticillioides resistance in maize by genomics-assisted breeding: Methods, progress, and prospects. Crop J. 2023, 11, 1626–1641. [Google Scholar] [CrossRef]
  8. European Food Safety Authority (EFSA). Scientific Opinion on the Risks for Public Health Related to the Presence of Fumonisins in Food. EFSA J. 2013, 11, 3443. [Google Scholar]
  9. Sabaly, S.; Tine, Y.; Diallo, A.; Faye, A.; Cisse, M.; Ndiaye, A.; Sambou, C.; Gaye, C.; Wele, A.; Paolini, J.; et al. Antifungal Activity of Cyperus articulatus, Cyperus rotundus and Lippia alba Essential Oils against Aspergillus flavus Isolated from Peanut Seeds. J. Fungi 2024, 10, 591. [Google Scholar] [CrossRef]
  10. Baranyi, N.; Kocsubé, S.; Vágvölgyi, C.; Varga, J. Current trends in aflatoxin research. Acta Biol. Szeged. 2013, 57, 95–107. [Google Scholar]
  11. Soares, C.; Rodrigues, P.; Peterson, S.W.; Lima, N.; Venacio, A. Three new species of Aspergillus section Flavi isolated from almonds and maize in Portugal. Mycologia 2012, 104, 682–697. [Google Scholar] [CrossRef]
  12. Stanković, S.; Lević, J.; Nikolić, M.; Krnjaja, V.; Jauković, M. Prvi Nalaz Aspergillus parasiticus u Proizvodnji Kukuruza u Srbiji. In Proceedings of the XIII Savetovanje o Zaštiti Bilja, Zlatibor, Serbia, 23–27 October 2015; pp. 32–33. [Google Scholar]
  13. Nikolić, M.; Savić, I.; Nikolić, A.; Stanković, G.; Delić, N.; Mladenović-Drinić, S.; Stanković, S. Maize resistance to ear rot caused by Aspergillus parasiticus. Genetika 2019, 51, 357–363. [Google Scholar] [CrossRef]
  14. Lević, J.; Gošić-Dondo, S.; Ivanović, D.; Stanković, S.; Krnjaja, V.; Bočarov-Stančić, A.; Stepanić, A. An Outbreak of Aspergillus Species in Response to Environmental Conditions in Serbia. Pestic. Phytomed. 2013, 28, 167–179. [Google Scholar] [CrossRef]
  15. Calvo, A.M.; Díez, A.J. Aspergillus species and their aflatoxins in maize production. Eur. J. Plant Pathol. 2009, 123, 343–353. [Google Scholar]
  16. European Food Safety Authority (EFSA). Scientific Opinion on the risks for public health related to the presence of aflatoxins in food. EFSA J. 2016, 14, 4595. [Google Scholar]
  17. Mielniczuk, E.; Skwaryło-Bednarz, B. Fusarium Head Blight, Mycotoxins and Strategies for Their Reduction. Agronomy 2020, 10, 509. [Google Scholar] [CrossRef]
  18. Ji, F.; He, D.; Olaniran, A.O.; Mokoena, M.P.; Xu, J.; Shi, J. Occurrence, toxicity, production and detection of Fusarium mycotoxin: A review. Food Prod. Process. Nutr. 2019, 1, 6. [Google Scholar] [CrossRef]
  19. Kumar, P.; Mahato, D.K.; Kamle, M.; Mohanta, T.K.; Kang, S.G. Aflatoxins: A Global Concern for Food Safety, Human Health and Their Management. Front. Microbiol. 2017, 7, 2170. [Google Scholar] [CrossRef]
  20. Akinola, S.A.; Ateba, C.N.; Mwanza, M. Behaviour of Aspergillus parasiticus in aflatoxin production as influenced by storage parameters using response surface methodology approach. Int. J. Food Microbiol. 2021, 357, 109369. [Google Scholar] [CrossRef]
  21. Wang, Y.; Wang, L.; Liu, F.; Wang, Q.; Selvaraj, J.N.; Xing, F.; Zhao, Y.; Liu, Y. Ochratoxin A Producing Fungi, Biosynthetic Pathway and Regulatory Mechanisms. Toxins 2016, 8, 83. [Google Scholar] [CrossRef]
  22. Bily, A.C.; Reid, L.M.; Savard, M.E.; Reddy, R.; Blackwell, B.A.; Campbell, C.M.; Krantis, A.; Durst, T.; Philogene, B.J.R.; Arnason, J.T.; et al. Analysis of Fusarium graminearum mycotoxins in different biological matrices by LC/MS. Mycopathologia 2004, 157, 117–126. [Google Scholar] [CrossRef]
  23. Rocha, O.; Ansari, K.; Doohan, F.M. Effects of trichothecene mycotoxins on eukaryotic cells: A review. Food Addit. Contam. 2005, 22, 369–378. [Google Scholar] [CrossRef]
  24. Kamle, M.; Mahato, D.K.; Devi, S.; Eun Lee, K.; Kang, S.G.; Kumar, P. Fumonisins: Impact on Agriculture, Food, and Human Health and their Management Strategies. Toxins 2019, 11, 328. [Google Scholar] [CrossRef] [PubMed]
  25. Stanković, S.; Lević, J.; Krnjaja, V. Fumonisin b1 in maize, wheat and barley grain in Serbia. Biotechnol. Anim. Husb. 2011, 27, 631–641. [Google Scholar] [CrossRef]
  26. Terciolo, C.; Bracarense, A.P.; Souto, P.C.M.C.; Cossalter, A.M.; Dopavogui, L.; Loiseau, N.; Oliveira, C.A.F.; Pinton, P.; Oswald, I.P. Fumonisins at Doses below EU Regulatory Limits Induce Histological Alterations in Piglets. Toxins 2019, 11, 548. [Google Scholar] [CrossRef]
  27. Kimanya, M.E.; Routledge, M.N.; Mpolya, E.; Ezekiel, C.N.; Shirima, C.P.; Gong, Y.Y. Estimating the risk of aflatoxin-induced liver cancer in Tanzania based on biomarker data. PLoS ONE 2021, 16, e0247281. [Google Scholar] [CrossRef] [PubMed]
  28. Marchese, S.; Polo, A.; Ariano, A.; Velotto, S.; Costantini, S.; Severino, L. Aflatoxin B1 and M1: Biological Properties and Their Involvement in Cancer Development. Toxins 2018, 10, 214. [Google Scholar] [CrossRef]
  29. Mahato, D.K.; Lee, K.E.; Kamle, M.; Devi, S.; Dewangan, K.N.; Kumar, P.; Kang, S.G. Aflatoxins in Food and Feed: An Overview on Prevalence, Detection and Control Strategies. Front. Microbiol. 2019, 10, 2266. [Google Scholar] [CrossRef]
  30. Battilani, P.; Toscano, P.; Van der Fels-Klerx, H.J.; Moretti, A.; Camardo Leggieri, M.; Brera, C.; Rortais, A.; Goumperis, T.; Robinson, T. Aflatoxin B1 contamination in maize in Europe increases due to climate change. Sci. Rep. 2016, 6, 24328. [Google Scholar] [CrossRef]
  31. Mitrović, I.; Grahovac, J.; Hrustić, J.; Jokić, A.; Dodić, J.; Mihajlović, M.; Grahovac, M. Utilization of waste glycerol for the production of biocontrol agents nigericin and niphimycin by Streptomyces hygroscopicus: Bioprocess development. Environ. Technol. 2021, 43, 3000–3013. [Google Scholar] [CrossRef]
  32. Silva, R.N.; Neves Monteiro, V.; Stecca Steindorff, A.; Vieira Gomes, E.; Ferreira Noronha, E.; Ulhoa, C.J. Trichoderma/pathogen/plant interaction in pre-harvest food security. Fungal Biol. 2019, 123, 565–583. [Google Scholar] [CrossRef]
  33. Harman, G.E. Myths and dogmas of biocontrol. Changes in perceptions derived from research on Trichoderma harzianum T-22. Plant Dis. 2000, 84, 377–393. [Google Scholar] [CrossRef] [PubMed]
  34. Shoresh, M.; Mastouri, F.; Harman, G.E. Induced systemic resistance and plant responses to fungal biocontrol agents. Annu. Rev. Phytopathol. 2010, 48, 21–43. [Google Scholar] [CrossRef] [PubMed]
  35. Harman, G.E. Trichoderma–not just for biocontrol anymore. Phytoparasitica 2011, 39, 103–108. [Google Scholar] [CrossRef]
  36. Zin, N.A.; Badaluddin, N.A. Biological functions of Trichoderma spp. for agriculture applications. Ann. Agric. Sci. 2020, 65, 168–178. [Google Scholar] [CrossRef]
  37. Al-Ani, L.K.T. Bioactive Secondary Metabolites of Trichoderma spp. for Efficient Management of Phytopathogens. In Secondary Metabolites of Plant Growth Promoting Rhizomicroorganisms; Bahadur Singh, H., Keswani, C., Reddy, M.S., Sansinenea, E., García-Estrada, C., Eds.; Springer Nature, Singapore Pte Ltd.: Singapore, 2019; pp. 125–143. [Google Scholar]
  38. Tančić Živanov, S.; Jevtić, R.; Lalošević, M.; Živanov, D.; Medić Pap, S.; Župunski, V. Efficacy of Trichoderma spp. against common fungal pathogens. Rat i Povrt. 2017, 54, 104–109. [Google Scholar] [CrossRef]
  39. Liu, J.B.; Gilardi, G.; Gullino, M.L.; Garibaldi, A. Effectiveness of Trichoderma spp. obtained from re-used soilless substrates against Pythium ultimum on cucumber seedlings. J. Plant Dis. Prot. 2009, 116, 156–163. [Google Scholar] [CrossRef]
  40. Vinale, F.; Sivasithamparam, K.; Ghisalberti, E.; Marra, R.; Woo, S.L.; Lorito, M. Trichoderma–plant–pathogen interactions. Soil Biol. Biochem. 2008, 40, 1–10. [Google Scholar] [CrossRef]
  41. Tucci, M.; Ruocco, M.; de Masi, L.; de Palma, M.; Lorito, M. The beneficial effect of Trichoderma spp. on tomato is modulated by the plant genotype. Mol. Plant Pathol. 2011, 12, 341–354. [Google Scholar] [CrossRef]
  42. Shukla, N.; Awasthi, R.P.; Rawat, L.; Kumar, J. Seed biopriming with drought tolerant isolates of Trichoderma harzianum promote growth and drought tolerance in Triticum aestivum. Ann. Appl. Biol. 2015, 166, 171–182. [Google Scholar] [CrossRef]
  43. Maisuria, K.M.; Patel, S.T. Seed germinability, root and shoot length and vigour index of soybean as influenced by rhizosphere fungi. Karnataka J. Agric. Sci. 2009, 22, 1120–1122. [Google Scholar]
  44. Asaduzzaman, M.; Alam, M.; Islam, M.M. Effect of Trichoderma on seed germination and seedling parameters of chili. J. Sci. Found. 2010, 8, 141–150. [Google Scholar] [CrossRef]
  45. Fungicide Resistance Action Committee (FRAC). 2016. Resistance Tables Benz. Available online: https://www.academia.edu/25340522/FRAC_Code_List_2016_Fungicides_sorted_by_mode_of_action_including_FRAC_Code_numbering (accessed on 25 May 2025).
  46. Lamichhane, J.; You, M.; Laudinot, V.; Barbetti, M.; Aubertot, J. Revisiting Sustainability of Fungicide Seed Treatments for Field Crops. Plant Dis. 2020, 104, 610–623. [Google Scholar] [CrossRef] [PubMed]
  47. Leslie, J.F.; Summerell, B.A. Fusarium laboratory workshops—A recent history. Mycotoxin Res. 2006, 22, 73–74. [Google Scholar] [CrossRef]
  48. Samuels, G.J.; Hebbar, P.K. Trichoderma: Identification and Agricultural Application; APS, USDA: St. Paul, MI, USA, 2015.
  49. Mitrović, I.; Vucurović, D.; Khalil Tawfeeq Al-Ani, L.; Mitrović, B.; Bajić, B.; Dodić, S.; Tančić Živanov, S. Production of Trichoderma harzianum K179 bioagent for maize diseases control: Complete laboratory stage bioprocess development. J. Appl. Microbiol. 2023, 134, lxad115. [Google Scholar] [CrossRef] [PubMed]
  50. Klich, M.A. Identification of Common Aspergillus Species; Centraalbureau voor Schimmelcultures (CBS) Fungal Biodiversity Centre, Royal Netherlands Academy of Arts and Sciences, Centraalbureau voor Schimmelcultures: Utrecht, The Netherlands, 2002; pp. 426–432. [Google Scholar]
  51. Grahovac, J.; Mitrović, I.; Dodić, J.; Grahovac, M.; Rončević, Z.; Dodić, S.; Jokić, A. Biocontrol agent for apple Fusarium rot: Optimization of production by Streptomyces hygroscopicus. Zemdirbyste 2020, 107, 263–270. [Google Scholar] [CrossRef]
  52. Reid, L.M.; Hamilton, R.I.; Mather, D.E. Screening Maize for Resistance to Gibberella Ear Rot; Research Branch Agriculture and Agri-Food Canada: Ottawa, ON, Canada, 1996; Technical Bulleten 5E. [Google Scholar]
  53. López-Valenzuela, B.E.; Armenta-Bojórquez, A.D.; Hernández-Verdugo, S.; Apodaca-Sánchez, M.A.; Samaniego-Gaxiola, J.A.; Valdez-Ortiz, A. Trichoderma spp. and Bacillus spp. as growth promoters in maize (Zea mays L.). Int. J. Exp. Bot. 2019, 88, 37–46. [Google Scholar]
  54. Milovac, Ž.; Zorić, M.; Franeta, F.; Terzić, S.; Petrović Obradović, O.; Marjanović Jeromela, A. Analysis of oilseed rape stem weevil chemical control using a damage rating scale. Pest Manag. Sci. 2017, 73, 1962–1971. [Google Scholar] [CrossRef]
  55. Sangeetha, G. Biological control potential of Trichoderma harzianum Rifai and Trichoderma viride Pers. ex S. F. Gray for the management of wilt of maize caused by Fusarium verticillioides (Nirenberg). J. Biol. Control. 2009, 23, 25–30. [Google Scholar]
  56. Degani, O.; Dor, S. Trichoderma Biological Control to Protect Sensitive Maize Hybrids against Late Wilt Disease in the Field. J. Fungi 2021, 7, 315. [Google Scholar] [CrossRef]
  57. Ferrigo, D.; Raiola, A.; Rasera, R.; Causin, R. Trichoderma harzianum seed treatment controls Fusarium verticillioides colonization and fumonisin contamination in maize under field conditions. Crop Prot. 2014, 65, 51–56. [Google Scholar] [CrossRef]
  58. Mitrović, B.; Drašković, B.; Stanisavljević, D.; Perišić, M.; Čanak, P.; Mitrović, I.; Tančić-Živanov, S. Environmental modeling of interaction variance for grain yield of medium early maturity maize hybrids. Genetika 2020, 52, 367–378. [Google Scholar] [CrossRef]
  59. Zhang, Z.; Wei, J.; Li, J.; Jia, Y.; Wang, W.; Li, J.; Lei, Z.; Gao, M. The impact of climate change on maize production: Empirical findings and implications for sustainable agricultural development. Front. Environ. Sci. 2022, 10, 954940. [Google Scholar] [CrossRef]
  60. Sabillón, L.; Alvarado, J.; Leiva, A.; Mendoza, R.; Espinal, R.; Leslie, J.F.; Bianchini, A. Presence, Co-Occurrence, and Daily Intake Estimates of Aflatoxins and Fumonisins in Maize Consumed in Food-Insecure Regions of Western Honduras. Toxins 2023, 15, 559. [Google Scholar] [CrossRef]
  61. Yates, I.E.; Meredith, F.; Smart, W.; Bacon, C.W.; Jaworski, A.J. Trichoderma viride Suppresses Fumonisin B1 Production by Fusarium moniliforme. J. Food Prot. 1999, 62, 1326–1332. [Google Scholar] [CrossRef]
  62. Rojo, F.; Ferez, M.; Reynoso, M.; Torres, A.; Chulze, S. Effect of Trichoderma species on growth of Fusarium proliferatum and production of fumonisins, fusaproliferin and beauvericin. Mycotoxin Res. 2007, 23, 173–179. [Google Scholar] [CrossRef] [PubMed]
  63. Ren, X.; Branà, M.T.; Haidukowski, M.; Gallo, A.; Zhang, Q.; Logrieco, A.F.; Li, P.; Zhao, S.; Altomare, C. Potential of Trichoderma spp. for Biocontrol of Aflatoxin-Producing Aspergillus flavus. Toxins 2022, 14, 86. [Google Scholar] [CrossRef] [PubMed]
  64. Dini, I.; Alborino, V.; Lanzuise, S.; Lombardi, N.; Marra, R.; Balestrieri, A.; Ritieni, A.; Woo, S.L.; Vinale, F. Trichoderma Enzymes for Degradation of Aflatoxin B1 and Ochratoxin A. Molecules 2022, 27, 3959. [Google Scholar] [CrossRef]
  65. Siri-anusornsak, W.; Kolawole, O.; Mahakarnchanakul, W.; Greer, B.; Petchkongkaew, A.; Meneely, J.; Elliott, C.; Vangnai, K. The Occurrence and Co-Occurrence of Regulated, Emerging, and Masked Mycotoxins in Rice Bran and Maize from Southeast Asia. Toxins 2022, 14, 567. [Google Scholar] [CrossRef]
  66. Tadijan, I.; Grahovac, J.; Dodić, J.; Grahovac, M.; Dodić, S. Effect of Cultivation Time on Production of Antifungal Metabolite(s) by Streptomyces hygroscopicus in Laboratory-Scale Bioreactor. J. Phytopathol. 2016, 164, 310–317. [Google Scholar] [CrossRef]
  67. Chiuraise, N.; Yobo, K.S.; Laing, M.D. Seed treatment with Trichoderma harzianum strain kd formulation reduced aflatoxin contamination in groundnuts. J. Plant Dis. Prot. 2015, 122, 74–80. [Google Scholar] [CrossRef]
  68. Kifle, M.H.; Yobo, K.S.; Laing, M.D. Biocontrol of Aspergillus flavus in groundnut using Trichoderma harzianum stain kd. J. Plant Dis. Prot. 2017, 124, 51–56. [Google Scholar] [CrossRef]
  69. Tian, Y.; Tan, Y.; Yan, Z.; Liao, Y.; Chen, J.; De Boevre, M.; De Saeger, S.; Wu, A. Antagonistic and Detoxification Potentials of Trichoderma Isolates for Control of Zearalenone (ZEN) Producing Fusarium graminearum. Front. Microbiol. 2018, 8, 2710. [Google Scholar] [CrossRef]
  70. Rawal, R.; Scheerens, J.C.; Fenstemaker, S.M.; Francis, D.M.; Miller, S.A.; Benitez, M.-S. Novel Trichoderma Isolates Alleviate Water Deficit Stress in Susceptible Tomato Genotypes. Front. Plant Sci. 2022, 13, 869090. [Google Scholar] [CrossRef] [PubMed]
  71. Saravanakumar, K.; Li, Y.; Yu, C.; Wang, Q.-q.; Wang, M.; Sun, J.; Gao, J.-X.; Chen, J. Effect of Trichoderma harzianum on maize rhizosphere microbiome and biocontrol of Fusarium Stalk rot. Sci. Rep. 2017, 7, 1771. [Google Scholar] [CrossRef]
  72. Sood, M.; Kapoor, D.; Kumar, V.; Sheteiwy, M.S.; Ramakrishnan, M.; Landi, M.; Araniti, F.; Sharma, A. Trichoderma: The “Secrets” of a Multitalented Biocontrol Agent. Plants 2020, 9, 762. [Google Scholar] [CrossRef]
  73. Republic Hydrometeorological Service of Serbia (RHMS). Available online: https://www.hidmet.gov.rs/index_eng.php (accessed on 12 July 2024).
  74. Kashyap, P.L.; Rai, P.; Srivastava, A.K.; Kumar, S. Trichoderma for climate resilient agriculture. World J. Microbiol. Biotechnol. 2017, 33, 155. [Google Scholar] [CrossRef]
  75. Chepsergon, J.; Mwamburi, L.; Kipkemboi Kassim, M. Mechanism of Drought Tolerance in Plants Using Trichoderma spp. Int. J. Sci. Res. 2012, 3, 1592–1595. [Google Scholar]
  76. Scudeletti, D.; Crusciol, C.A.C.; Bossolani, J.W.; Moretti, L.G.; Momesso, L.; Servaz Tubaña, B.; de Castro, S.G.Q.; De Oliveira, E.F.; Hungria, M. Trichoderma asperellum Inoculation as a Tool for Attenuating Drought Stress in Sugarcane. Front. Plant Sci. 2021, 12, 645542. [Google Scholar] [CrossRef]
  77. Zaidi, N.W.; Dar, M.H.; Singh, S.; Singh, U.S. Trichoderma Species as Abiotic Stress Relievers in Plants. In Biotechnology and Biology of Trichoderma; Gupta, V.K., Schmoll, M., Herrera-Estrella, A., Upadhyay, R.S., Druzhinina, I., Tuohy, M.G., Eds.; Elsevier: Amsterdam, The Netherlands, 2014; pp. 515–525. [Google Scholar] [CrossRef]
  78. Cornejo-Ríos, K.; Osorno-Suárez, M.d.P.; Hernández-León, S.; Reyes-Santamaría, M.I.; Juárez-Díaz, J.A.; Pérez-España, V.H.; Peláez-Acero, A.; Madariaga-Navarrete, A.; Saucedo-García, M. Impact of Trichoderma asperellum on Chilling and Drought Stress in Tomato (Solanum lycopersicum). Horticulturae 2021, 7, 385. [Google Scholar] [CrossRef]
  79. Tyskiewicz, R.; Nowak, A.; Ozimek, E.; Jaroszuk-Sciseł, J. Trichoderma: The Current Status of Its Application in Agriculture for the Biocontrol of Fungal Phytopathogens and Stimulation of Plant Growth. Int. J. Mol. Sci. 2022, 23, 2329. [Google Scholar] [CrossRef]
  80. Jambhulkar, P.P.; Raja, M.; Singh, B.; Katoch, S.; Kumar, S.; Sharma, P. Potential native Trichoderma strains against Fusarium verticillioides causing post flowering stalk rot in winter maize. Crop Prot. 2022, 152, 105838. [Google Scholar] [CrossRef]
Figure 1. Immersion treatment (a), treatment with a coating machine (b), and sowing (c).
Figure 1. Immersion treatment (a), treatment with a coating machine (b), and sowing (c).
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Figure 2. Antagonistic activity of T. harzianum K179 cultivation broth (107 CFU/mL) against A. flavus (a) and F. graminearum (b); controls (c).
Figure 2. Antagonistic activity of T. harzianum K179 cultivation broth (107 CFU/mL) against A. flavus (a) and F. graminearum (b); controls (c).
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Figure 3. Cumulative probabilities of the proportional odds model for different treatments for hybrid NS 2662 from the POM (2021).
Figure 3. Cumulative probabilities of the proportional odds model for different treatments for hybrid NS 2662 from the POM (2021).
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Figure 4. Cumulative probabilities of the proportional odds model for different treatments for hybrid NS 2662 from the POM (2022).
Figure 4. Cumulative probabilities of the proportional odds model for different treatments for hybrid NS 2662 from the POM (2022).
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Figure 5. Grain yield for hybrid NS 2662 during the 2021 and 2022 growing seasons. Values in the same year followed by the same letter are not statistically significantly different at the 0.05 level.
Figure 5. Grain yield for hybrid NS 2662 during the 2021 and 2022 growing seasons. Values in the same year followed by the same letter are not statistically significantly different at the 0.05 level.
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Table 1. Parameter estimates of the proportional odds model for disease severity across different treatments (results for 2021).
Table 1. Parameter estimates of the proportional odds model for disease severity across different treatments (results for 2021).
TreatmentβLower CIUpper CIp
T2−0.8710−1.7423−0.02460.046
T3−3.8406−4.9900−2.78240.000
T4−5.4154−6.8135−4.16150.000
T5−4.5105−5.7601−3.37260.000
Table 2. Coefficient estimates of the proportional odds model for disease severity across different treatments (results for 2022).
Table 2. Coefficient estimates of the proportional odds model for disease severity across different treatments (results for 2022).
TreatmentβLower CIUpper CIp
T2−0.559−1.4040.2740.201
T3−1.908−2.870−0.9930.000
T4−3.402−4.609−2.3020.000
T5−2.543−3.612−1.5500.000
Table 3. Presence of mycotoxins in maize samples from the 2021 growing season.
Table 3. Presence of mycotoxins in maize samples from the 2021 growing season.
μg/kgAflatoxinsOchratoxin AZENDONFumonisinsHT-2T-2
B1B2G1G2B1B2
MI T1<0.4<0.4<0.4<0.4<1.6<16<6411,4194384<9.6<9.6
MII T1<0.4<0.4<0.4<0.4<1.6<16<6490373895<9.6<9.6
MI T2<0.4<0.4<0.4<0.4<1.6<16<6410,8483698<9.6<9.6
MII T2<0.4<0.4<0.4<0.4<1.6<16<6435059241478692
MI T3<0.4<0.4<0.4<0.4<1.6<16<6438221405<9.6<9.6
MII T3<0.4<0.4<0.4<0.4<1.6<16<642126660<9.6<9.6
MI T4<0.4<0.4<0.4<0.4<1.6<16<642813981<9.6<9.6
MII T4<0.4<0.4<0.4<0.4<1.6<16<642164896<9.6<9.6
MI T5<0.4<0.4<0.4<0.4<1.6<16<641982709<9.6<9.6
MII T5<0.4<0.4<0.4<0.4<1.6<16<641491368<9.6<9.6
Table 4. Results of the presence of mycotoxins in maize samples from the 2022 growing season.
Table 4. Results of the presence of mycotoxins in maize samples from the 2022 growing season.
μg/kgAflatoxinsOchratoxin AZENDONFumonisinsHT-2T-2
B1B2G1G2B1B2
MI T12.90.6<0.4<0.4<1.619<6460432704<9.6<9.6
MII T13.20.8<0.4<0.4<1.623<6425,86712,569<9.6<9.6
MI T20.80.5<0.4<0.4<1.6<16<6410,6434552<9.6<9.6
MII T20.60.4<0.4<0.4<1.6<16<6436641582<9.6<9.6
MI T3<0.4<0.4<0.4<0.4<1.6<16<6476592780<9.6<9.6
MII T3<0.4<0.4<0.4<0.4<1.6<16<6414,1285790<9.6<9.6
MI T4<0.4<0.4<0.4<0.4<1.6<16<6465262347<9.6<9.6
MII T4<0.4<0.4<0.4<0.4<1.6<16<6462233028<9.6<9.6
MI T5<0.4<0.4<0.4<0.4<1.6<16<6487654455<9.6<9.6
MII T5<0.4<0.4<0.4<0.4<1.6<16<6459392423<9.6<9.6
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Mitrović, I.; Čanak, P.; Tančić Živanov, S.; Farkaš, H.; Vasiljević, M.; Ćujić, S.; Zorić, M.; Mitrović, B. Trichoderma harzianum in Biocontrol of Maize Fungal Diseases and Relevant Mycotoxins: From the Laboratory to the Field. J. Fungi 2025, 11, 416. https://doi.org/10.3390/jof11060416

AMA Style

Mitrović I, Čanak P, Tančić Živanov S, Farkaš H, Vasiljević M, Ćujić S, Zorić M, Mitrović B. Trichoderma harzianum in Biocontrol of Maize Fungal Diseases and Relevant Mycotoxins: From the Laboratory to the Field. Journal of Fungi. 2025; 11(6):416. https://doi.org/10.3390/jof11060416

Chicago/Turabian Style

Mitrović, Ivana, Petar Čanak, Sonja Tančić Živanov, Hunor Farkaš, Marko Vasiljević, Svetlana Ćujić, Miroslav Zorić, and Bojan Mitrović. 2025. "Trichoderma harzianum in Biocontrol of Maize Fungal Diseases and Relevant Mycotoxins: From the Laboratory to the Field" Journal of Fungi 11, no. 6: 416. https://doi.org/10.3390/jof11060416

APA Style

Mitrović, I., Čanak, P., Tančić Živanov, S., Farkaš, H., Vasiljević, M., Ćujić, S., Zorić, M., & Mitrović, B. (2025). Trichoderma harzianum in Biocontrol of Maize Fungal Diseases and Relevant Mycotoxins: From the Laboratory to the Field. Journal of Fungi, 11(6), 416. https://doi.org/10.3390/jof11060416

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