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Article

Impacts of Gaseous Ozone (O3) on Germination, Mycelial Growth, and Aflatoxin B1 Production In Vitro and In Situ Contamination of Stored Pistachio Nuts

1
Department of Biology, College of Science, Taif University, P.O. Box 11099, Taif 21944, Saudi Arabia
2
Applied Mycology Group, Environment and AgriFood Theme, Cranfield University, Cranfield MK43 0AL, UK
*
Author to whom correspondence should be addressed.
Toxins 2022, 14(6), 416; https://doi.org/10.3390/toxins14060416
Submission received: 22 May 2022 / Revised: 12 June 2022 / Accepted: 15 June 2022 / Published: 17 June 2022
(This article belongs to the Special Issue Reduction and Control of Mycotoxins along Entire Food and Feed Chain)

Abstract

:
Pistachio nuts can become colonized by mycotoxigenic fungi, especially Aspergillus flavus, resulting in contamination with aflatoxins (AFs). We examined the effect of gaseous O3 (50–200 ppm; 30 min; 6 L/min) on (a) in vitro germination, (b) mycelial growth, and (c) aflatoxin B1 (AFB1) production on a milled pistachio nut-based medium at different water activity (aw) levels and at 30 °C. This was complimented with in situ studies exposing raw pistachio nuts to 50–200 ppm of O3. Exposure of conidia to gaseous O3 initially resulted in lower germination percentages at different aw levels. However, 12 h after treatment, conidial viability recovered with 100% germination after 24–48 h. Growth rates of mycelial colonies were slightly decreased with the increase of the O3 dose, with significant inhibition only at 0.98 aw. The production of AFB1 after O3 treatment and storage for 10 days was stimulated in A. flavus colonies at 0.98 aw. Raw pistachio nuts inoculated with A. flavus conidia prior to O3 exposure showed a significant decrease in population after 20 days of storage. However, AFB1 contamination was stimulated in most O3 treatments. The relationship between exposure concentration, time and prevailing aw levels on toxin control needs to be better understood for these nuts.
Key Contribution: This is the first detailed study of the potential for the use of gaseous ozone treatment to try and control different life-cycle phases of A. flavus on milled raw pistachio-based media and in situ control of A. flavus populations and aflatoxin B1 in raw stored shelled pistachio nuts when treated and stored under different water activity conditions.

1. Introduction

Ozone (O3) is commonly generated in the summer because of the reactions between photochemicals in the atmosphere in the presence of sunlight. O3 gas has been commonly used in the food industry for sanitizing packaging materials, raw materials, and storage facilities [1]. It has been suggested that the advantage of O3 over other remedial chemicals used in foodstuffs is that it is residue-free. It decomposes to diatomic oxygen rapidly because of its short half-life, which is about 20–50 min in the atmosphere and 1–10 min in water [2]. However, it is a very corrosive gas, and for its use, it is critical that appropriate tubing (PTFE), steel, or glass systems are used. Manning and Teidemann [3] showed that small increases in ozone (O3) concentrations (40–60 ppb) can influence the mycobiota of plant surfaces and perhaps the biosynthesis of toxins. Slight increases in exposure to gaseous O3 as a pollutant was previously shown to change the phyllosphere mycobiota on conifer needles [4].
At the present time, the EU legislation established a maximum level of 12 μg/kg aflatoxin B1 (AFB1) in nuts, including pistachios used for processing, and 8 μg/kg AFB1 for direct human consumption [5]. The AF contamination of pistachio nuts occurs either pre-harvest, because of early splitting of the shells and insect damage, or during subsequent drying and processing [6]. For example, in Iran, an analysis of 10,000+ samples of pistachio nuts showed AFB1 in 36%, with almost 12% exceeding the maximum level in Iran (5 μg/kg) [7]. In Algeria, between 1998 and 2002, the highest AFB1 in 523 samples was 113 μg/kg, with a mean range of 1 to 3.8 μg/kg [8]. In Tunisia, 76% of pistachio nuts were found to be contaminated with AFs during storage [9]. Delayed harvesting and processing and storage has been shown to significantly influence and often increase the AFB1 contamination of pistachio nuts [6,10]. Thus, there has been interest in examining treatments such as gaseous O3 for the mitigation of AFs in nuts, including pistachios [11,12,13].
Some previous studies have examined the efficiency of electrochemically-generated O3 on the activity of aflatoxigenic fungi and aflatoxin (AFs) in different nuts, including peanuts and brazil nuts. However, there are less studies on pistachio nuts [11,12,13]. Mylona et al. [14] showed that gaseous O3 (100–400 ppm) was not very effective against the microconidal germination of Fusarium verticiilioides in vitro, but it was able to reduce fumonisin B1 (FB1) contamination in stored maize grain after treatment. Indeed, the initial inhibition of germination was followed by recovery, growth, and FB1 production. However, Sultan et al. [12] found that gaseous O3 was very effective in inhibiting the germination of conidia of A. flavus, but it had little efficacy in controlling the mycelial growth of A. flavus strains on peanut-based media, regardless of water activity (aw). Studies have been carried out on the O3 treatment of Brazil nuts and showed that exposure to this gas affected the growth of the mycobiota and decreased AFs [11]. They used three concentrations of O3 (10, 14, and 31.5 mg/L) for five hours and found that this inhibited colonization by both A. flavus and A. parasiticus over a storage period of 180 days. However, at low concentrations of O3, the fungi were still able to grow. Care is needed with nuts because the high concentration of lipids can interact with gaseous O3, resulting in tainting and off-flavors [15]. The sensitivity of fungal species to O3 exposure may vary and depends on the exposure period, concentration applied, and type of commodity. It can also be influenced by moisture content and spore morphology [16,17].
No previous studies have examined the effect of gaseous O3 (0–200 ppm) as a control measure for germination, colonization, and AFB1 in raw milled pistachio-based media or in stored raw pistachios. Thus, the aim of this study was to examine the use of gaseous O3 to control (a) in vitro conidial germination, (b) in vitro mycelial growth and AFB1 production, and (c) A. flavus populations on raw pistachio nuts when inoculated with conidia of this species and exposed to O3 and the effects on subsequent AFB1 contamination after 20 days of storage at different aw levels.

2. Results

2.1. Effect of O3 on Conidial Germination of A. flavus In Vitro on a Milled Pistachio-Based Medium

The mean germination of conidia of A. flavus was influenced by gaseous O3 treatment, regardless of the aw level used (Figure 1). However, all the O3-treated conidia showed a recovery in germination capacity after 48 h, regardless of aw level. The only exceptions were the samples treated with 200 ppm O3 at 0.98 aw and all O3 doses at 0.93 aw after 12 h.

2.2. In Vitro Effect of Gaseous O3 Treatment on Mycelial Growth

The mycelial extension of A. flavus (strain AB3) was significantly inhibited after O3 treatment when compared with the control at 0.98 aw (Figure 2). However, the growth rates with the different O3 exposure concentrations were relatively similar. At 0.93 aw, growth rates were slightly higher after O3 treatment, with little difference between the concentrations of O3 used.

2.3. In Vitro Effect of Gaseous O3 Exposure of Colonies of A. flavus on AFB1 Production

The AFB1 productions were significantly higher after O3 treatments at all exposure levels when compared to the untreated control in the 0.98 aw treatments (Figure 3). However, at 0.93 aw, there was no significant effect on toxin production, with much lower AFB1 productions on the raw pistachio-based medium.

2.4. In Situ Effects of Gaseous O3 Treatment on Populations of A. flavus in Stored Raw Pistachio Nuts

The total populations of A. flavus slightly increased in the control samples when exposed to air (Figure 4). However, there was a significant reduction in the A. flavus CFUs from Log10 5.3 CFUs (control after exposure to air) to Log10 1.4 CFUs, after exposure to 50 ppm O3, and <Log10 1.0 CFUs after 100 and 200 ppm O3 exposure at 0.98 aw. For pistachio nuts at 0.93 aw, the A. flavus populations remained very similar regardless of the gaseous O3 treatment. At both the aw levels, it seemed that higher O3 doses (100, 200 ppm) did not have any increased efficacy when compared to 50 ppm O3 exposure.

2.5. In Situ Effects of O3 Treatment on AFB1 Contamination of Raw Stored Pistachio Nuts

The AFB1 contamination was found to always be higher in the treated samples compared to the controls at both aw levels and all gaseous O3 exposure levels, except for 50 ppm (Figure 5). At this concentration and 0.98 aw, the AFB1 was significantly reduced.

3. Discussion

3.1. In Vitro Effects on Germination and Mycelial Extension

The efficacy of gaseous O3 for the control of conidial germination and mycelial growth of A. flavus strains (AB3, AB10) was evaluated in this study on a milled raw pistachio nut-based medium at different aw levels. The aw levels chosen were based on ecological data, which showed that optimum A. flavus growth occurs at >0.97 aw and optimum AFB1 at >0.94 aw at 25–30 °C. For the prevention of toxin contamination, pistachio nuts would need to be dried to <0.88 aw [18]. Overall, exposure of conidia to O3 initially had lower germination percentages when compared to the controls at both the aw levels. Treatment with 200 ppm O3 at 0.98 aw showed the complete inhibition of germinations after 12 h; however, spore viability appeared to recover, and the germination was increased after 24 h and reached 100% germination after 48 h. Sultan and Magan [12] found that there was an effective inhibition of conidial germination by O3 treatment of A. flavus strains from peanuts with complete inhibition at 200–250 ppm O3 (6 L/min; 30 min). However, this was on a defined yeast extract sucrose medium. Previously, Mylona et al. [14] examined the in vitro effect of O3 treatment at 100 and 200 ppm for 30 min (6 L/min) on the spore germination of F. verticillioides. Although germinative capacity was inhibited after 24 h, over the following 72 h there was a recovery, and after 8–10 days at both 0.98 and 0.94 aw, FB1 production occurred. They also found that doubling the exposure time (60 min) did not improve the efficacy of O3. Indeed, recent studies with species from the Aspergillus section Circumdati and Nigri responsible for the ochratoxin A contamination of coffee showed tolerances of up to 500 ppm O3 [19]. It has been suggested that O3 acts by oxidizing vital cellular components, especially unsaturated lipids in cell membranes, resulting in a leakage of cell contents and subsequent microbial lysis at high concentrations [20,21]. However, some of these studies have been performed in O3-treated water and not with gaseous O3 [12].
For mycelial growth, the present study showed that the mycelial extension was inhibited by O3 exposure at 0.98 aw. However, growth rates decreased only slightly with the increasing O3 dose. Very few studies have examined the in vitro effect on the growth of A. flavus, and none were on nut-based media [12]. A previous study by Zotti et al. [22] found that O3 treatment of 3-day-old A. flavus colonies for 3 h inhibited growth and spores completely. However, when the same colony reached 6 and 9 days old, the efficacy decreased. Additionally, they found that there are different sensitivity levels among species, with A. flavus being less sensitive than A. niger. However, in their study, aw modification was not considered and the O3 concentration used was only 1 ppm. Akbar et al. [19] found that the mycelial extension of strains of A. carbonarius and A. westerdijkiae in coffee-based medium with up to 500 ppm of O3 had little effect on the rates of colonization, regardless of aw level used or exposure period (30–60 min).
The general tolerance of aflatoxigenic and ochratoxigenic Aspergillus spp. to O3 may in part be due to the darker pigmentation and relatively thick-walled conidia, which can provide protection against UV-light, sunlight, and toxic gases. In addition, the capacity for relatively rapid DNA repair after exposure may be quite rapid, allowing the viability of conidia to be conserved after exposure. This could be related to both pigmentation and/or repair systems that help the cells to recover viability. Indeed, Hibben and Stotzky [16] indicated that small hyaline spores are more sensitive to O3, while large and pigmented spores, such as the conidia of A. niger, were more resistant [23,24]. Spores of A. fumigatus have been found to be particularly resistant to O3 [18]. In contrast, spores of Fusarium species (e.g., F. verticillioides, F. langsethiae), which are practically hyaline and have very little pigmentation, appear to be sensitive to O3 exposure in air initially, although some recovery of viability was found [9]. A thorough comparison amongst species belonging to the same genus is important.
Reduction of fungal growth can be obtained in high moisture conditions after treatment with up to 1000–15,000 ppm O3 for 1 h [25]. For Brazil nuts, O3 treatment was found to affect the growth of the mycobiota and to decrease aflatoxin contamination levels [26]. However, the exposure period was 5 h, which was effective and inhibited the growth of A. flavus and A. parasiticus, although they were still able to grow during the initial few days after O3 exposure. Thus, O3 levels and exposure time together with the other influencing factors, including temperature and ERH, need to be examined in more detail to optimize the potential use of this gas for control of the key life cycle phases of mycotoxigenic spoilage fungi and toxin production [21].

3.2. In Vitro and In Situ Effects of O3 on AFB1 Contamination

In the present study, AFB1 was analyzed after the in vitro exposure of colonies of A. flavus to O3 for 30 min and then stored for 10 days at 30 °C. There appeared to be variable effects on AFB1 production by exposure to O3 treatment. The increase in toxins may be due to O3 exposure acting as an environmental stress, resulting in the biosynthesis of more toxins as a defense reaction. In addition, it may be that the O3 interacts with the pistachio-based medium, changing the nutritional make up, especially in relation to fatty acids. Sultan and Magan [12] examined A. flavus exposure to O3 (100–300 ppm) on a conducive YES medium. In this case, the use of a defined medium and exposure to O3 resulted in a significant decrease of AFB1 production in mycelial colonies. However, they examined toxin biosynthesis after 3 days, while the present study examined it for 10 days on a pistachio-nut based medium to simulate the natural nutritional conditions as far as was possible. This could explain the differences observed. Previously, Mason et al. [2] showed that the exposure of A. flavus colonies for 5 days inhibited asexual conidial sporulation. This suggested that perhaps the effect of O3 on the whole life cycle of A. flavus would provide useful information on which phase might be more sensitive to such treatment [27]. The present study is the first to examine in detail the in situ effect of gaseous O3 on the colonization and toxin production by A. flavus in stored pistachio nuts. Overall, while to populations of A. flavus significantly decreased due to O3 exposure, there was little difference between 50–200 ppm treatment levels. Indeed, a reduction in AFB1 was only observed in the 50 ppm O3 × 0.98 aw treatment. It may be that a reduction in overall populations of A. flavus allows more rapid subsequent colonization by the surviving inoculum of the rich nutrient source. In naturally contaminated pistachio nuts, the mycobiota is varied with a range of fungi present [28]. Thus, the niche will be occupied by a fungal community including A. flavus, and it would have to compete with these other fungi, some of which may survive O3 treatment. A previous study exposed pistachio nuts and ground nuts artificially contaminated with aflatoxins to very low concentrations of O3 (5–9 mg/L = 2–5 ppm gaseous O3) for 140 and 420 min [10]. They found that AFB1 and total aflatoxins were reduced by about 23 and 24%, respectively, with the highest O3 treatment level (9 mg/L) for 420 min. The treatments were much less effective against ground pistachios [15]. However, these studies were only carried out at 70% relative humidity, and spiking with the toxins is not the same as natural occurrence in this commodity due to colonization by the mycotoxigenic species. Thus, further studies are required to better understand the relationship between commodity type, exposure concentration × time of exposure, and prevailing aw level to determine efficacy in terms of toxin control [13].
The studies by Mylona et al. [14] certainly suggest that the natural contamination of maize grain with fumonisins can be reduced by exposure to O3 concentrations. However, it may be more difficult to reduce mycotoxin production by specific fungi without longer term exposure to O3. Indeed, even with 500 ppm, O3 was found to have relatively little effect on the reduction of ochratoxin A contamination of stored green coffee contaminated with A. westerdijkiae and A. carbonarius and stored under different aw levels at 30 °C [19]. Savi et al. [27] found that the exposure of wheat to 40–60 mg/L of O3 for up to 180 min reduced the growth of F. graminearum significantly, with deoxynivalenol in the pericarp and endosperm tissue being completely inhibited. However, the moisture content of the grain was not considered in these studies, which are important relative to colonization by Fusaria and trichothecene production. It is, however, important to consider that food ozonation may not always be a beneficial process, especially where this gaseous treatment may alter food sensory characteristics, color, cause lipid oxidation, and the degradation of phenolic compounds and vitamins [29,30].

4. Conclusions

This study has shown that the use of gaseous O3 exposure of both conidia and mycelial colonies of A. flavus on a milled raw pistachio nut-based medium was not very effective. Indeed, via repair systems, the conidia recovered germinative capacity rapidly. Up to 200 ppm of gaseous O3 for 30 min had little impact on mycelial extension and subsequent AFB1 production. In situ studies with stored raw pistachio nuts inoculated with A. flavus conidia and exposed to O3 reduced the isolation of the A. flavus populations but had little effect on AFB1 contamination after 20 days of storage at different aw levels. This suggests that perhaps much longer exposure times may be required and that the efficacy may also be influenced by the moisture content and the type of commodity, in this case a lipid-rich matrix. However, this would have to be balanced against potential tainting effects and eating quality, which might be impacted if high exposure levels are used for longer time periods. In the future, for more effective and safe use in food processing, the optimum gaseous O3 concentration, contact time, and other treatment conditions need to be defined for specific foods. Pilot scale tests would probably need to be conducted for each commodity before potential commercial application, as every food application with O3 application may be different.
In addition, in vitro and in vivo toxicological tests need to be conducted to quantify the effects of degradation products on human and animal health.

5. Materials and Methods

5.1. Apparatus for Ozone Generation and Experimental System

O3 was generated in the laboratory using a C-Lasky series O3 generator purchased from AirTree Ozone Technology Co. (model CL010DS), Sijhih, Taiwan. This equipment generates O3 by corona discharge between two tubs, with no metals involved for efficiency improvement, generation stability, and less energy consumption. The generated O3 was directed into the exposure chamber using a Teflon tube, which was properly connected to the generator. For safety reasons, the experiment was carried out in a fume cupboard to prevent O3 from spreading into the laboratory atmosphere. Two different systems were used for O3 exposure for in vitro and in situ assays. O3 concentration was measured using an O3 analyzer (Model UV-100, Eco Sensor, Santa Fe, NM, USA), which was connected to the chamber to measure the exit gas accurately. It should be noted that 1 ppm of O3 generated is equivalent to 2.14 mg/L of O3 in the air. This allows for comparison with some other studies. Experimental set-ups were performed as follows:
(a)
The exposure system of O3 for in vitro germination and mycelial growth assays was a 5-L airtight glass jar. The O3 inlet of the system was connected from the generator to the lid of the jar using a Teflon tube, which was inserted into the bottom of the jar. The outlet of the system was also in the lid of the jar and connected to the O3 analyzer using a Teflon tube. This ensured accurate measurement of the O3 concentrations in the glass container. The flow rate of the generated O3 used was 6 L/min for 30 min.
(b)
Exposure system of O3 for the in situ study.
The exposure chamber for in situ experiments was a 100-mL volume glass tube. The tube was capable of containing about 45–50 g of pistachio nuts. These were placed inside the column, and the O3 was forced upwards via an inlet at the bottom of the tube coming from the generator. The outlet at the top was connected to the O3 analyzer and vented in the fume hood. This allowed accurate exposure of the pistachio nuts to the treatment O3 concentrations for the necessary residence time. The flow rate of generated O3 was 6 L/min for 30 min.

5.2. Fungal Strains, Media, Spore Suspension, and Water Activity

One strain of A. flavus (AB3), representative of 3–4 others isolated from pistachio nuts, was used in these studies [13,31]. This was chosen as it was representative of those studied previously [13,31]. Pistachio-based media were used for spore germination and mycelial growth studies. A 3%-milled raw pistachio nut agar (PMA) was used with 2% technical agar (Thermo Fisher Scientific Oxoid Ltd., Basingstoke, Hampshire, UK) [13].
For spore suspension, fresh cultures of the AB3 strain were prepared on PMA and incubated at 25 °C for 5–7 days. AB3 culture surfaces were gently scraped and transferred into sterile Universal vials containing sterile water + 0.1% Tween 80 solution (Tween 80 (ACROS organics). The concentration of the spore suspension was determined using a hemocytometer (Olympus BX40 microscope, Microoptical Co., Sauerlach, Germany; slide Marienfeld superior, Germany; microscope glass cover slips, No 3, 18 mm × 18 mm, Chance proper Ltd., Malvern, Worcestshire, UK) and adjusted by dilution to 107 spores/mL. Target aw values (0.98 and 0.93) for PNA were obtained by using glycerol/water solutions, instead of water, to modify the aw with this non-ionic solution. For these two treatments, the equivalent of 122.5 and 355 g of glycerol per L of water was used. This was mixed, and the mixture was used similar to water.

5.3. Effect of O3 on Conidial Spore Germination of A. flavus

Four different treatments were examined, including three concentrations of O3: 0, 50, 100, 200 ppm of O3 at the two different aw levels detailed previously and incubated at 30 °C. Samples exposed to the air were used as controls for each aw. The experiment was carried out in triplicate and repeated once. An amount of 100 µL of 106 spore suspension was spread onto PNA media treatments and replicates and allowed to dry. Lids were taken off the plates and the media were placed inside the airtight glass jar for O3 exposure for 30 min at a flow rate of 6 L/min, as described previously. The Petri plates were separated by 2–3 cm to ensure exposure of each plate. After exposure, plates were placed into plastic boxes, which were maintained at the same aw levels with glycerol/water solutions (500 mL × 2) and stored at 30 °C. Three agar plugs were taken every 12 h from each plate using a surface-sterilized cork-borer (1 cm) and placed on a glass microscope slide (Fisherbrand, Leicestershire, UK). The agar plugs were then stained with Lactophenol Cotton Blue (ProLab Diagnostics, Birkenhead, UK) and covered with a glass coverslip. Each plug was then examined under the microscope, and germination was recorded. Spores were considered to have germinated when the length of the germ tube was longer than the diameter of the spore. A total of 3 × 50 single spores per replicate were examined (450 per treatment). The overall mean number of germinated spores (out of 50) was calculated for the different O3 treatments.

5.4. In Vitro Effects of Gaseous O3 on Mycelial Growth and AFB1 Contamination

PNA media were inoculated centrally with 10 µL of spore suspension made from AB3 strain and incubated at 30 °C in replicates and allowed to grow for 2 and 5–6 days in the 0.98 and 0.93 aw treatments, respectively. Measurements of colonies were recorded, and plates were exposed to O3 with no lids for 30 min using the system described previously. The O3 concentrations were 50, 100, and 200, with air as a control. Aw of media and ERH during incubation after O3 exposure was adjusted to 0.93 and 0.98 aw. After exposure, Petri plates were covered with the lids and incubated at 30 °C. Colony diameters were recorded on a daily basis for each treatment and compared with the control. Agar plugs were taken after day ten from each replicate and stored at −20 °C for AFB1 analysis.

5.5. In Situ Effect of Gaseous O3 on Fungal Population and AFB1 Production on Irradiated Pistachio Nuts

Irradiated raw pistachio nuts (12–15 KGys; Synergy Health Sterilisation UK Ltd., Swindon, Wiltshire, UK) were weighed and place in sterilized bottles (eight bottles) for each treatment (40 g per replicate). The absence of any fungal contaminants was checked by direct-plating individual pistachio nuts on Malt Extract Agar medium (MEA; Thermo Fisher Scientific Oxoid Ltd., Basingstoke, Hampshire, UK) and incubated for 7 days at 25 °C. This showed no contamination. The raw pistachio nuts were rewetted using a moisture adsorption curve [25] and mixed well and left overnight at 4 °C to equilibrate to the target aw levels of 0.93 and 0.98. A conidial suspension of 106 spores was prepared. After equilibration, 1 mL of the spore suspension was added to the pistachio nuts and mixed well. Small sub-samples were taken (1 g) and placed in 10 mL of sterile water containing tween 80 in a 25 mL Universal bottle for serial dilution to assess the populations of A. flavus present. Three separate replicates of each treatment (40 g each) were exposed to O3 (50, 100, and 200 ppm, or air) for 30 min at a flow rate of 6 L/min.
Immediately after exposure, sub-samples were taken for serial dilution of the populations. The rest of the pistachio nuts were placed in solid culture vessels with microporous lids (Magenta, Sigma Ltd., Coventry, UK). These were previously autoclaved at 121 °C for 15 min with aluminum foil covers. The glass chambers containing the treatments/replicates were then placed in plastic chambers with glycerol/water solutions to maintain the target ERH (93 and 98% ERH) and stored for 20 days at 30 °C. Samples were taken for A. flavus fungal populations after this storage period. The remaining pistachio nuts were stored at −20 °C for later AFB1 analysis.
For serial dilution, samples were soaked for 20 min and then vigorously shaken using a vortex mixer. From each treatment/replicate serial dilutions were made. For each concentration, three replicates were made, and 100 µL was spread on MEA media using a sterile spreader and incubated at 30 °C for 7 days before colonies were counted for A. flavus populations.

5.6. Aflatoxin B1 Quantification

Preparation of aflatoxin standards: A 200-μL stock solution of aflatoxins (B1, B2, G1, G2) standard in methanol containing 250 ng AFB1 was prepared and pipetted into 2-mL Eppendorf tubes for overnight evaporation until dryness in a fume hood similar to the samples.

5.6.1. In Vitro Aflatoxin B1 Analyses

Colony Extraction: Initially, agar plugs were cut out across the diameter of colonies using a surface-sterilized 4-mm diameter cork-borer (approx. 4–6). The agar plugs were placed in pre-weighed 2-mL Eppendorf tubes and weighed again. Five-hundred μL of HPLC-grade chloroform was added to the tubes and shaken for 30 min using a KS 501 digital orbital shaker (IKA (R) Werke GmbH & Co. KG, Esslingen, Germany). The chloroform extract was transferred to a new Eppendorf tube and dried gently under air for derivatization.
Derivatization of aflatoxin B1 extract: Derivatization of the AFB1 extract was performed according to the AAOC method [32]. First, 200 μL of hexane was added to the tube, followed by 50 μL of trifluoroacetic acid. The mixture was vortexed for 30 s and left for 5 min. A mixture of water:acetonitrile (9:1) was then added to the tube, vortexed for 30 s, and left for 10 min to allow for separation of the layers. Then, the aqueous layer was filtered using a syringe nylon filter (13 mm × 0.22 μm; Jaytee Biosciences Ltd., Herne Bay, UK) into amber-salinized 2-mL HPLC vials (Agilent, Santa Clara, CA, USA) before HPLC analysis. All analytical reagents used were HPLC-grade.
Quantification of aflatoxin B1 with High Performance Liquid Chromatography HPLC: A reverse-phase HPLC with fluorescence detection was used to confirm the identity and quantify AFB1. An Agilent 1200 series HPLC system was used for the analysis. It consisted of an in-line degasser, auto sampler, binary pump, and a fluorescence detector (excitation and emission wavelengths of 360 and 440 nm, respectively). Separation was achieved using a C18 column (Phenomenex Gemini; 150 × 4.6, 3 μm particle size; Phenomenex, Torrance, CA, USA) with a Phenomenex Gemini C18 3 mm, 3-μm guard cartridge. Isocratic elution with methanol:water:acetonitrile (30:60:10, v/v/v) as the mobile phase was performed at a flow rate of 1.0 mL/min. The injection volume was 20 µL. A set of standards was injected (1 to 5 ng AFB1, AFB2, AFG1, and AFG2 per injection), and standard curves were generated by plotting the area underneath the peaks against the amounts of AFB1 standard injected. The run time for the each HPLC analysis was 12 min. Supplementary Figure S1 shows an example of a standard and a sample for aflatoxin B1 quantification.

5.6.2. Quantification of Aflatoxin B1 in Pistachio Nuts

The pistachio nut samples were all dried in a drying oven at 50 °C in the dark. They were subsequently ground (Waring blender, Merck Ltd., Feltham, UK) and weighed (25 g). The background aflatoxin B1 level in the nuts used in the experiments was 0.015 ng/g. This was taken into account as a correction factor in the final quantification of the results. Acetonitrile/water 60/40 (100 mL) was used as an extraction solvent. The mixture was blended for 3 min, and the extract was filtered into a smaller sample container. PBS buffer (pH 7.4, Thermo Fisher Scientific) was used for sample dilution, then the diluted extract was passed through an Immunoaffinity Column (IAC; AflaStar™; Romer Labs, Tulln an der Donau, Austria) with a flow rate between 1–3 mL/min. The column was rinsed with 2 × 10 mL sterile distilled water. HPLC-grade methanol (1.5–3 mL) was then applied to the column, and the eluent was collected in a new amber glass vial and left to dry overnight at room temperature before the derivatization step, as detailed previously.

5.7. Statistical Analysis

Three replicates per treatment were used in all studies and repeated once. Means were obtained by taking the average of three measurements for each experiment with the standard error of the means (±SE; standard error) obtained. Analysis of variance (ANOVA) was applied to analyze the variation of means with a 95% confidence interval. Normal distribution of data was checked by the normality test Kolmogorov-Smirnov, using Minitab statistical software. Fisher’s Least Significant Difference (LSD) was used to identify differences between the means, with p < 0.05 as a significant difference, using the same statistical software.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/toxins14060416/s1, Figure S1: Examples of HPLC analyses of (a) a standard and (b) a sample of pistachio nut-based agar for aflatoxin B1 quantification.

Author Contributions

A.B. carried out the research work and analyses of the data as part of his Ph.D. thesis in the Applied Mycology Group and wrote the initial draft manuscript; A.M. was involved as co-supervisor of the project and the mycotoxin analyses and contributed to the draft manuscript; N.M. developed the original project and conceptualization of the work, was the primary supervisor of the project, and revised the manuscript for the final submitted version. All authors have read and agreed to the published version of the manuscript.

Funding

The current work was funded by Taif University Researchers Supporting Project number (TURSP-2020/295), Taif university, Taif, Saudi Arabia.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The raw data used in this study and the statistical analyses are available via the corresponding author at Cranfield University.

Acknowledgments

The authors are grateful to Taif University Researchers Supporting Project Number (TURSP-2020/295), Taif University, Taif, Saudi Arabia for funding this research which was carried out in the Applied Mycology Group, Cranfield University, United Kingdom.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. United States Food and Drug Administration. Code of Federal Regulations: Maximum Acceptable Level of Ozone; 21CFR801.415; United States Food and Drug Administration: Silver Spring, MD, USA, 2019; Volume 8. Available online: https://www.accessdata.fda.gov/scripts/cdrh/cfdocs/cfcfr/cfrsearch.cfm?fr=801.415 (accessed on 22 May 2022).
  2. Mason, L.J.; Woloshuk, C.P.; Maier, D.E. Efficacy of ozone to control insects, molds and mycotoxins. In Proceedings of the International Conference on Controlled Atmosphere and Fumigation in Stored Products, Nicosia, Cyprus, 21–26 April 1997; Donahaye, E.J., Navarro, S., Varnava, A., Eds.; Printer Ltd.: Nicosia, Cyprus, 1997; pp. 665–670. [Google Scholar]
  3. Manning, W.J.; Tiedemann, A.V. Climate change: Potential effects of increased atmospheric Carbon dioxide (CO2), ozone (O3), and ultraviolet-B (UVB) radiation on plant diseases. Environ. Pollut. 1995, 88, 219–245. [Google Scholar] [CrossRef]
  4. Magan, N.; Kirkwood, I.A.; McLeod, A.R.; Smith, M.K. Effect of sulphur dioxide and ozone on phyllosphere and endophytic fungi of conifer needles. Plant Cell Environ. 1995, 18, 291–302. [Google Scholar] [CrossRef]
  5. European Commission Regulation. No. 165/2010 Amending Regulation (EC) No 1881/2006 Setting Maximum Limits for Certain Contaminants in Foodstuffs as Regards Aflatoxins. 2010. Available online: https://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2010:050:0008:0012:EN:PDF (accessed on 5 May 2022).
  6. Georgiadou, M.; Dimou, A.; Yanniotis, S. Aflatoxin contamination in pistachio nuts: A farm to storage study. Food Control 2012, 26, 580–586. [Google Scholar] [CrossRef]
  7. Cheraghali, A.M.; Yazdanpanah, H.; Doraki, N.; Abouhossain, G.; Hassibi, M.; Ali Abadi, S.; Aliakbarpoor, M.; Amirahmadi, M.; Askarian, A.; Fallah, N.; et al. Incidence of aflatoxins in Iran pistachio nuts. Food Chem. Toxicol. 2007, 45, 812–816. [Google Scholar] [PubMed]
  8. Fernane, F.; Sanchis, V.; Marin, S.; Ramos, A.J. First Report on Mould and Mycotoxin Contamination of Pistachios Sampled in Algeria. Mycopathologia 2010, 170, 423–429. [Google Scholar]
  9. Ghali, R.; Hmaissia-Khlifa, K.; Ghorbel, H.; Maaroufi, K.; Hedili, A. Incidence of aflatoxins, ochratoxin A and zearalenone in Tunisian foods. Food Control 2008, 19, 921–924. [Google Scholar]
  10. Esmaeilpour, A.; Shakerardekani, A. Effect of Harvesting Time and Delay in the Hulling Process on the Aflatoxin Content of Pistachio Nuts. J. Food Qual. 2022, 2022, 7831016. [Google Scholar] [CrossRef]
  11. Giordano, B.N.E.; Nones, J.; Scussel, V.M. Susceptibility of the In-shell Brazil Nut Mycoflora and Aflatoxin Contamination to Ozone Gas Treatment during Storage. J. Agric. Sci. 2012, 4, 2012. [Google Scholar]
  12. Sultan, Y.; Magan, N. Potential for control of A. flavus and aflatoxin B1 in vitro and in stored Egyptian shelled peanuts using gaseous ozone treatment. Sci. Technol. Cereals Oils Foods 2021, 29, 29–37. [Google Scholar]
  13. Afsah-Hejri, L.; Hajeb, P.; Ehsani, R.J. Application of ozone for degradation of mycotoxins in food: A review. Compr. Rev. Food Sci. Food Saf. 2020, 19, 1777–1808. [Google Scholar] [CrossRef]
  14. Mylona, K.; Kogkaki, E.; Sulyok, M.; Magan, N. Efficacy of gaseous ozone treatment on spore germination, growth and fumonisin production by Fusarium verticillioides in vitro and in situ in maize. J. Stored Prod. Res. 2014, 59, 178–184. [Google Scholar] [CrossRef]
  15. Akbas, M.Y.; Ozdemir, M. Effect of different ozone treatments on aflatoxin degradation and physicochemical properties of pistachios. J. Sci. Food Agric. 2006, 86, 2099–2104. [Google Scholar] [CrossRef]
  16. Hibben, C.R.; Stotzky, G. Effects of ozone on the germination of fungus spores. Can. J. Microbiol. 1969, 15, 1187–1196. [Google Scholar] [CrossRef] [PubMed]
  17. Antony-Babu, S.; Singleton, I. Effects of ozone exposure on the xerophilic fungus, Eurotium amstelodami IS-SAB-01, isolated from naan bread. Int. J. Food Microbiol. 2011, 144, 331–336. [Google Scholar] [CrossRef]
  18. Baazeem, A.; Garcia-Cela, E.; Medina, A.; Magan, N. Interacting abiotic factors affect growth and aflatoxin B1 production profiles of strains of Aspergillus flavus on pistachio-based matrices and stored pistachio nuts. Front. Microbiol. 2021, 11, 624007. [Google Scholar] [CrossRef]
  19. Akbar, A.; Medina, A.; Magan, N. Potential control of mycotoxigenic fungi and ochratoxin A in stored coffee using gaseous ozone treatment. Microorganisms 2020, 8, 1462. [Google Scholar] [CrossRef]
  20. Conte, G.; Fontanelli, M.; Galli, F.; Cotrozzi, L.; Pagni, L.; Pellegrini, E. Mycotoxins in feed and food and the role of ozone in their detoxification and degradation: An update. Toxins 2020, 12, 486. [Google Scholar] [CrossRef]
  21. Guzel-Seydim, Z.B.; Greene, A.K.; Seydim, A.C. Use of ozone in the food industry. LWT-Food Sci. Technol. 2004, 37, 453–460. [Google Scholar] [CrossRef]
  22. Zotti, M.; Porro, R.; Vizzini, A.; Mariotti, M.G. Inactivation of Aspergillus spp. by ozone treatment. Ozone Sci. Eng. 2008, 30, 423–430. [Google Scholar] [CrossRef]
  23. Restaino, L.; Frampton, E.W.; Hemphill, J.B.; Palnikar, R. Efficacy of ozonated water against various food related microorganisms. Appl. Environ. Microbiol. 1995, 61, 3471–3475. [Google Scholar] [CrossRef] [Green Version]
  24. Whistler, P.E.; Sheldon, B.W. Biocidal activity of ozone versus formaldehyde against poultry pathogens inoculated in a prototype setter. Poult. Sci. 1989, 68, 1068–1073. [Google Scholar] [CrossRef] [PubMed]
  25. White, S.D.; Murphy, P.T.; Leandro, L.F.; Bern, C.J.; Beattie, S.E.; van Leewen, J.H. Mycoflora of high moisture maize treated with ozone. J. Stored Prod. Res. 2013, 55, 84–89. [Google Scholar] [CrossRef]
  26. Giordano, B.N.E.; Simao, V.; Manfio, D.; Galvao, S.; Scussel, J.N.; Scussel, V.M. Reduction of in-shell Brazil nut (Bertholletia excelsa H.B.K.) aflatoxin contamination by ozone gas application during storage. Julius-Kühn-Archiv 2010, 425, 574–580. [Google Scholar]
  27. Savi, G.D.; Piacentini, K.C.; Bittencourt, K.O.; Scussel, V.M. Ozone treatment efficiency on Fusarium graminearum and deoxynivalenol degradation and its effects on whole wheat grains (Triticum aestivum L.) quality and germination. J. Stored Prod. Res. 2014, 59, 245–253. [Google Scholar] [CrossRef]
  28. Roushdy, M.M.; Abdel-Shakour, E.H.; Abdel-Ghany, T.M. Sporicidal Effect of Ozone on Fungal and Bacterial Spores in Water Disinfection. J. Am. Sci. 2011, 7, 942–948. [Google Scholar]
  29. Zhu, F. Effect of ozone treatment on the quality of grain products. Food Chem. 2019, 264, 358–366. [Google Scholar] [CrossRef] [PubMed]
  30. Prudente, A.D., Jr.; King, J.M. Efficacy and safety evaluation of ozonation to degrade aflatoxin in corn. J. Food Sci. 2002, 67, 2866–2872. [Google Scholar]
  31. Baazeem, A. Ecology, Climate Change and Control Strategies for Aspergillus flavus Colonisation and Aflatoxin Contamination of Pistachio Nuts. Ph.D. Thesis, Applied Mycology Group, Cranfield University, Cranfield, UK, 2018. [Google Scholar]
  32. Kok, W.T. Derivatization reactions for the determination of aflatoxins by liquid chromatography with fluorescence detection. J. Chromatogr. B Biomed. Sci. Appl. 1994, 659, 127–137. [Google Scholar] [CrossRef] [Green Version]
Figure 1. Effect of gaseous ozone (6 L/min for 30 min) on the mean number of conidia of A. flavus strain AB3 germinating (mean of 9 × 50 conidia) at 0.98 and 0.93 aw on a 3% milled raw pistachio nut medium and then incubated at 30 °C. Bars indicate the SEM number of spores germinated.
Figure 1. Effect of gaseous ozone (6 L/min for 30 min) on the mean number of conidia of A. flavus strain AB3 germinating (mean of 9 × 50 conidia) at 0.98 and 0.93 aw on a 3% milled raw pistachio nut medium and then incubated at 30 °C. Bars indicate the SEM number of spores germinated.
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Figure 2. Effect of gaseous ozone treatment on the mycelial colony extension rate of A. flavus (strain AB3) on a 3% milled raw pistachio nut-based medium at 0.98 and 0.93 water activity (aw) and 30 °C for 4–6 days. Colonies were exposed to gaseous ozone for 30 min at 6 L/min prior to incubation. Different letters indicate significant differences (p < 0.05). Bars indicate mean SE.
Figure 2. Effect of gaseous ozone treatment on the mycelial colony extension rate of A. flavus (strain AB3) on a 3% milled raw pistachio nut-based medium at 0.98 and 0.93 water activity (aw) and 30 °C for 4–6 days. Colonies were exposed to gaseous ozone for 30 min at 6 L/min prior to incubation. Different letters indicate significant differences (p < 0.05). Bars indicate mean SE.
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Figure 3. Effect of ozone treatment on AFB1 production by A. flavus (strain AB3) at 0.93 and 0.98 aw on a raw milled pistachio-based medium after 10 days at 30 °C. Colonies were exposed to ozone for 30 min at 6 L/min prior to incubation. Different letters indicate significant differences (p < 0.05).
Figure 3. Effect of ozone treatment on AFB1 production by A. flavus (strain AB3) at 0.93 and 0.98 aw on a raw milled pistachio-based medium after 10 days at 30 °C. Colonies were exposed to ozone for 30 min at 6 L/min prior to incubation. Different letters indicate significant differences (p < 0.05).
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Figure 4. Populations of A. flavus (strain AB3, Log10 CFUs) isolated from ozonized raw pistachio nut samples before and after treatment and storage for 20 days. Exposure to O3 was for 30 min at 6 L/min prior to incubation. Different letters indicate significant differences (p < 0.05).
Figure 4. Populations of A. flavus (strain AB3, Log10 CFUs) isolated from ozonized raw pistachio nut samples before and after treatment and storage for 20 days. Exposure to O3 was for 30 min at 6 L/min prior to incubation. Different letters indicate significant differences (p < 0.05).
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Figure 5. Effect of ozone exposure on AFB1 contamination of raw pistachio nuts inoculated with A. flavus strain AB3 at 0.93 and 0.98 aw then stored for 4 weeks after treatment at 30 °C. The pistachio nuts were exposed to gaseous ozone for 30 min at 6 L/min prior to storage. Different letters indicate significant differences between treatments (p < 0.05).
Figure 5. Effect of ozone exposure on AFB1 contamination of raw pistachio nuts inoculated with A. flavus strain AB3 at 0.93 and 0.98 aw then stored for 4 weeks after treatment at 30 °C. The pistachio nuts were exposed to gaseous ozone for 30 min at 6 L/min prior to storage. Different letters indicate significant differences between treatments (p < 0.05).
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Baazeem, A.; Medina, A.; Magan, N. Impacts of Gaseous Ozone (O3) on Germination, Mycelial Growth, and Aflatoxin B1 Production In Vitro and In Situ Contamination of Stored Pistachio Nuts. Toxins 2022, 14, 416. https://doi.org/10.3390/toxins14060416

AMA Style

Baazeem A, Medina A, Magan N. Impacts of Gaseous Ozone (O3) on Germination, Mycelial Growth, and Aflatoxin B1 Production In Vitro and In Situ Contamination of Stored Pistachio Nuts. Toxins. 2022; 14(6):416. https://doi.org/10.3390/toxins14060416

Chicago/Turabian Style

Baazeem, Alaa, Angel Medina, and Naresh Magan. 2022. "Impacts of Gaseous Ozone (O3) on Germination, Mycelial Growth, and Aflatoxin B1 Production In Vitro and In Situ Contamination of Stored Pistachio Nuts" Toxins 14, no. 6: 416. https://doi.org/10.3390/toxins14060416

APA Style

Baazeem, A., Medina, A., & Magan, N. (2022). Impacts of Gaseous Ozone (O3) on Germination, Mycelial Growth, and Aflatoxin B1 Production In Vitro and In Situ Contamination of Stored Pistachio Nuts. Toxins, 14(6), 416. https://doi.org/10.3390/toxins14060416

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