Authors: Eva María Mateo (1Department of Microbiology and Ecology, Faculty of Medicine and Odontology, University of Valencia, 46010 Valencia, Valencia, Spain), Fernando Mateo (fernando.mateo@uv.es), Andrea Tarazona (andrea.tarazona@uv.es), Misericordia Jiménez (andrea.tarazona@uv.es)
Categories: Review, metal nanoparticles, toxigenic fungi, mycotoxins, prevention, control
Source: Toxins
Authors: Eva María Mateo, Fernando Mateo, Andrea Tarazona, Misericordia Jiménez
Mycotoxins are secondary metabolites produced primarily by certain species of the genera Aspergillus, Fusarium, Penicillium, Alternaria, and Claviceps. Toxigenic fungi and mycotoxins are prevalent in staple foods, resulting in significant economic losses and detrimental impacts on public health and food safety. These fungi demonstrate remarkable adaptation to water and heat stress conditions associated with climate change, and the use of synthetic antifungals can lead to the selection of resistant strains. In this context, the development of novel strategies for their prevention and control of food is a priority objective. This review synthesizes the extant knowledge concerning the antifungal and anti-mycotoxin potential of the primary metal nanoparticles (silver, copper) and metal oxide nanoparticles (copper oxide and zinc oxide) studied in the literature. It also considers synthesis methods and the lack of consensus on technical definitions and regulations. Despite methodological gaps and the scarcity of publications analyzing the effect of these NPs on fungal growth and mycotoxin production simultaneously, it can be concluded that these NPs present high reactivity, stability, and the ability to combat these food risks. However, aspects related to their biosafety and consumer acceptance remain major challenges that must be addressed for their implementation in the food industry.
The extent of fungal diversity remains to be elucidated. It is estimated that the number of species ranges from 2.2 to 3.8 million [1], and up to 5.1 million [2]. Fungal diseases are responsible for more than 1.5 million deaths per year, which is more than three times the number of deaths caused by malaria and comparable to the number of deaths caused by tuberculosis [3] and breast cancer [4]. Human fungal pathogens are regarded as the “hidden killers” of the medical community, given their ability to cause a multitude of infections and complications in human health [3,4,5,6,7]. The accelerated proliferation of fungal infections is often associated with climate change, the virulence of the pathogens, and the increasing prevalence of immunocompromised patients worldwide [8,9]. Therefore, the timely recognition and treatment of such infections are of significant importance and necessitate the availability of comprehensive information in this regard.
Within the domain of food security and safety, toxigenic fungi emerge as the most significant pathogens of global concern [10]. These fungi, belonging to the genera Aspergillus, Fusarium, Penicillium, Alternaria, and Claviceps [11], can, under certain conditions, produce mycotoxins that accumulate in grains, fruits, and other foodstuffs. Mycotoxins are highly toxic compounds affecting both humans and animals. The mechanisms of action and health effects of mycotoxins on human and animal health have been the subject of study for many years. Most mycotoxins are known to exert harmful effects on animals and/or humans, such as immunotoxic, genotoxic, cytotoxic, neurotoxic, teratogenic, or carcinogenic outcomes [12,13,14,15,16,17,18]. Toxigenic fungi are generally phytopathogens, and their mycotoxins commonly contaminate staple foods in both human and animal diets [19,20,21]. These fungi and their toxins substantially impact the economy and public health [22,23,24,25], causing significant damage to crops [26]. Losses from contamination of agricultural commodities by fungi and mycotoxins pose serious threats to food safety [12,27,28]. Mycotoxin contamination is particularly alarming in regions heavily reliant on staple foods such as grains, cereals, and nuts. Safeguarding a sustainable food supply depends on preventing mycotoxin contamination.
Within the domain of crop mycobiota, there is a close relationship between the prevailing fungal populations, regional climatology, agricultural practices, and the types and levels of mycotoxins present. Cereals and cereal products such as bread, pasta, breakfast cereals, cake, snacks, beer, infant food, complete feed, and pet foods harbor the greatest diversity of mycotoxin-producing species simultaneously, and consequently, the widest array of mycotoxins [29,30,31,32,33,34,35,36]. However, other commonly consumed foods, beverages, or food additives also represent important sources of mycotoxins. These include nuts and dried fruits [37,38,39,40,41,42,43,44], coffee [45,46,47,48,49,50], cocoa [51], spices [52,53,54,55], milk and derivatives [56,57,58,59], grapes and grape-derived items [60,61,62,63], meat and meat products [64,65,66,67,68], among others.
Several hundred mycotoxins are known; however, only a subset is regulated in the European Union (EU) for specific foods and beverages considered most susceptible to contamination, as they consist of raw materials or their derivatives that commonly host the producing fungi [19,69,70,71]. The mycotoxins regulated in the EU and their principal fungal sources are as aflatoxin B1 (AFB1), the sum of aflatoxins B1, B2, G1, and G2 (AFB1, AFB2, AFG1, and AFG2), and aflatoxin M1 (AFM1) produced by Aspergillus flavus, A. parasiticus, and A. nonius; ochratoxin A (OTA) produced by A. niger, A. carbonarius, A. welwitschiae, A. steynii, A. ochraceus, A. westerdijkiae, Penicillium verrucosum, and P. nordicum; the sum of fumonisins B1 and B2 (FB1 and FB2) produced by Fusarium verticillioides, F. proliferatum and A. niger; patulin (PAT) produced by P. expansum; deoxynivalenol (DON) and zearalenone (ZEA) formed by F. graminearum and F. culmorum; citrinin (CIT) produced by Penicillium citrinum, Monascus purpureus, and M. ruber; the sum of T-2 and HT-2 toxins (T-2 and HT-2) produced by F. sporotrichioides and F. langsethiae; and ergot alkaloids (EA) associated with Claviceps spp. These regulated mycotoxins represent those most frequently detected in susceptible foodstuffs and are under EU control due to their established toxicity profiles and prevalence. In addition, the content of ergot sclerotia in unprocessed cereal grains is also regulated in the EU [72,73,74]. Other unregulated mycotoxins are attracting growing attention from the scientific community. These include the Fusarium mycotoxins nivalenol (NIV), diacetoxyscirpenol (DAS), enniatins (ENs), beauvericin (BEA), moniliformin, and fusaproliferin; the Aspergillus toxins sterigmatocystin and emodin; and the Alternaria metabolites alternariol and tenuazonic acid [75,76].
Toxigenic fungi are highly competitive species that adapt well to water and heat stress conditions associated with climate change [76,77,78]. For example, aflatoxin-producing strains of Aspergillus flavus show optimal growth temperatures and aflatoxin production at temperatures between 33 °C and 37 °C, under low water activity (aw) conditions [79,80,81]. Moreover, the simultaneous presence of multiple mycotoxins within an agricultural commodity leads to interactions (antagonistic, additive, or synergistic) that can amplify toxicity beyond what is observed from individual toxins alone [82,83,84,85,86].
Preventing and controlling fungal growth and mycotoxin production and accumulation in food is not an easy task because many biotic and abiotic factors and mutual interactions are involved [87,88] (Figure 1).
The elimination of mycotoxins from foodstuffs is a multifaceted process, given their remarkable resistance to various food-processing techniques, including cooking, boiling, baking, frying, roasting, pasteurization, and extrusion [89]. Consequently, in recent years, machine learning (ML) methods have been investigated to predict fungal growth and mycotoxin production by relevant toxigenic fungi under different environmental conditions [90,91,92,93,94,95,96,97,98].
Despite extensive scientific efforts to elucidate the complex interactions between fungi and the biotic-abiotic factors of their environment (Figure 1), the risks posed by toxigenic fungi and mycotoxins in foods have not been eliminated; in some cases, they have increased and are expected to continue rising in the medium term under new climate change scenarios [76,77,78]. The latest Intergovernmental Panel on Climate Change (IPCC) Sixth Assessment report confirms that global warming is unequivocal, accompanied by unprecedented climatic changes [99]. These environmental shifts can significantly influence the life cycles of toxigenic fungi, altering host resistance and host–pathogen interactions [100,101]. As a result, the resilience of diverse toxigenic species and their capacity for mycotoxin synthesis could be profoundly affected.
Undoubtedly, the primary strategy for mitigating the risks associated with toxigenic fungal colonization of food and mycotoxin accumulation is to prevent fungal growth at all stages of the food chain, including pre-harvest and post-harvest processes such as drying, transportation, packaging, storage, and marketing. A diverse array of physical, chemical, and biological methods has been employed to control mycotoxin contamination, including innovative and emerging technologies such as ionizing and non-ionizing radiation, cold plasma, pulsed light, ultrasound, pulsed electric fields, high-pressure processing, and essential oils [102,103]. Among these methods, the use of antifungal compounds remains the most effective strategy.
Conventional synthetic antifungals have several they produce toxic residues that can harm the environment, beneficial microbes, and both humans and animals [104]. Additionally, their use can lead to the development of resistant strains. Furthermore, low doses of certain fungicides may sometimes promote mycotoxin production by specific fungal species [105,106].
Despite the existence of a variety of commercial synthetic antifungal agents, their utilization is constrained by factors such as their toxicity and the emergence of multidrug-resistant strains [27,104,107,108,109,110]. The rate of antifungal resistance development has been characterized as “unprecedented.” This phenomenon can be attributed, at least in part, to the considerable medical advancements that have transpired over the past few decades. Examples of such advancements include the discovery of antibiotics, significant progress in cancer treatment, and the development of surgical transplants. The HIV epidemic and the global pandemic of the novel coronavirus (SARS-CoV-2) have led to a notable increase in the number of individuals with compromised immune systems. This rise has consequently resulted in a shift in the epidemiology of fungal infections, which have transitioned from being sporadic etiological agents of disease to becoming a significant contributor to human morbidity and mortality on a global scale. Individuals with compromised immune systems are predisposed to a greater incidence of fungal infections in comparison with those who are healthy [108,111]. Currently, there are approximately 80 types of antifungal drugs available for clinical use. These compounds can be categorized into five classes, including polyenes, allylamines, azoles, pyrimidine analogues, and echinocandins. In comparison with antibiotics, the number of antifungal agents is limited. Azoles are utilized for a variety of purposes, including the protection of human, animal, and crop health, as well as the formulation of antifouling coatings and wood preservatives [112]. The extensive utilization of azoles has accelerated the emergence of azole-resistant fungi, which has substantial ramifications for human health and food security [27,112]. Fungi have developed several resistance mechanisms. They include alterations of drug targets and cellular pathways (e.g., sterol biosynthesis), reductions of intercellular concentrations of target enzymes, overexpression of the antifungal drug target, activation of stress response signaling, and overexpression of efflux pump proteins. Furthermore, fungi possess intrinsic mechanisms of resistance to antifungal drugs. These mechanisms include biofilm formation, variations in cellular permeability, and many processes that overlap with those involved in acquired resistance. These include target incompatibility, stress response signaling, and the expression of efflux pump proteins [27,113,114]. A pre-harvest strategy to mitigate mycotoxin presence in plant-derived foods involves resistance to fungal infection by toxigenic fungi. Genetic modifications have led to the development of plant varieties that exhibit full or partial resistance to Fusarium spp. infection. For example, overexpression of the antifungal gene HvNEP-1 in the endosperm renders barley less susceptible to Fusarium head blight, resulting in lower mycotoxin levels in the grain [115]. Highly resistant wheat cultivars can convert DON into deoxynivalenol-3-glucoside, a compound that is less toxic than DON [116]. A significant reduction in total mycotoxin content has been observed in transgenic maize cultivars compared to their non-transgenic counterparts. These findings suggest that the consumption of transgenic maize may pose a reduced risk of mycotoxin contamination [117].
The lack of efficacious antifungal drugs, combined with mounting resistance, has created an urgent need for novel treatments. Consequently, alternative eco-friendly and effective agents are under continuous investigation. Developing antifungal strategies that are economically viable, sustainable, and safe presents a significant challenge. In this context, nanotechnology holds considerable potential to advance these strategies. Combining the use of resistant cultivars with approaches that reduce mycotoxin accumulation and biosynthesis can lower mycotoxin levels in cereals [118].
The field of nanotechnology is defined as the scientific and engineering discipline focused on the design, fabrication, and utilization of structures, devices, and systems through the manipulation of atoms and molecules at the nanoscale level. The synthesis, management, and application of nanomaterials fall under the interdisciplinary umbrella of nanotechnology. In the 21st century, this field has experienced rapid development, leading to significant advancements across various scientific disciplines. Nanomaterials have garnered considerable attention due to their unique properties and extensive applications in multiple sectors. They are utilized in food processing and food preservation/packaging, food fortification, functional food additives, and sensors [119,120,121,122]; in agriculture, including insecticides, herbicides, fungicides, fertilizers, and plant growth regulators, as well as in food safety, water purification, and biosensors for agronomic troubleshooting [123,124,125,126,127,128,129,130,131,132,133,134,135,136,137,138,139,140,141,142,143]; in medicine, encompassing drug delivery, diagnostics, tissue engineering, antimicrobials, and gene delivery [144,145,146,147,148,149]; in environmental applications, including bioremediation and catalysts in environment [129,150,151,152,153,154,155], and various other industries, such as electronics, automotive, defense, and cosmetics [156].
Currently, nanoparticles (NPs) with antifungal properties are highly valued for their diverse applications. However, their use in the agri-food sector remains largely unexplored [157]. Specifically, there is a need to review the existing knowledge regarding their effects on mycotoxin-producing species and the production of mycotoxins. The fields of nanotechnology and toxigenic fungi intersect in various ways, particularly in the context of addressing mycotoxins. Research indicates that NPs represent a promising strategy for controlling toxigenic fungi and mycotoxins in food [158]. This approach not only enhances the efficacy of antifungal compounds but also reduces toxicity, improves stability, and facilitates targeted delivery.
In light of the contemporary challenges posed by toxigenic fungi and mycotoxins in food products, addressing this complexity necessitates the development of innovative management strategies. This review aims to provide a comprehensive overview of the potential of metallic nanoparticles (MNPs) as effective agents for the prevention and control of toxigenic fungi and mycotoxins in food products. Specifically, this review focuses on silver nanoparticles (AgNPs), copper nanoparticles (CuNPs), copper oxide nanoparticles (CuONPs), and zinc oxide nanoparticles (ZnONPs), as these have demonstrated the highest efficacy in existing studies. The chemical and thermal stability of inorganic NPs is superior to that of organic NPs, making them more suitable for storage, transportation, and use in harsh environments.
What exactly constitutes a nanoparticle (NP) remains a topic of considerable debate. The International Organization for Standardization (ISO) classifies nanoparticles as nano-objects, which are materials whose external dimensions fall within the nanoscale. If these dimensions exceed the nanoscale by a factor of three or more, they are more accurately referred to as “nanofibers” or “nanoplates” rather than nanoparticles [159]. Similarly, the Scientific Committee on Consumer Products (SCCP) defines NPs as particles with at least one dimension ranging from 1 to 100 nm [160]. Nevertheless, there is still no universal agreement on the definition of “nanoparticle,” which complicates related processes [161].
Nanomaterials can originate from natural sources, arise unintentionally through human activities, or be deliberately engineered to exhibit novel properties, such as enhanced strength, chemical reactivity, or conductivity, due to their nanoscale structure. The European Union has enacted legislation to clearly define these materials and assess the potential health and environmental risks associated with their applications. Additionally, the risk assessment bodies and agencies of the European Union have developed guidance for evaluating nanomaterials. The Commission Recommendation C/2022/3689 [162] provides a comprehensive definition of nanomaterials that revises and replaces the previous nanomaterial definition established in Commission Recommendation 2011/696/EU [163]. According to this recommendation, ’Nanomaterial’ refers to a “natural, incidental or manufactured material consisting of solid particles that are present, either on their own or as identifiable constituent particles in aggregates or agglomerates, and where 50% or more of these particles in the number-based size distribution fulfill at least one of the following (a) one or more external dimensions of the particle are in the size range of 1 nm to 100 nm; (b) the particle has an elongated shape, such as a rod, fiber or tube, where two external dimensions are smaller than 1 nm and the other dimension is larger than 100 nm; (c) the particle has a plate-like shape, where one external dimension is smaller than 1 nm and the other dimensions are larger than 100 nm”.
Specifically regarding food, Commission Regulation (EU) 2015/2283 [164] defines “engineered nanomaterial” as any intentionally produced material with one or more dimensions on the order of 100 nm or less, or composed of discrete functional parts, internally or at the surface, many of which have one or more dimensions on the order of 100 nm or less, including structures, agglomerates, or aggregates that may exceed 100 nm in size but retain properties characteristic of the nanoscale. This aligns closely with Commission Recommendation C(2022)3689 [159], but key distinctions include the (1) its specific reference to “engineered” nanomaterials, and (2) the absence of a minimum percentage threshold (e.g., ≥50%) for classification. To support implementation, some measures have been (1) reviewing modern methodologies; (2) advancing analytical method development and validation for the detection of nanomaterials in food; and (3) providing Member States with training and analytical support. Furthermore, different manufacturing methods for engineered nanoparticles can yield variations in loading capacity, delivery efficiency, and shelf life.
In the academic literature, nanomaterials are commonly categorized by morphology, size, and chemical composition [165]. Based on chemical composition, NPs are typically grouped into three inorganic, organic, and carbon-based.
Inorganic NPs are defined by the absence of carbon-based compounds. Examples include metal, ceramic, and semiconductor NPs. MNPs, whether single-metal, bimetallic, or polymetallic, are composed of metal atoms, whereas metal oxide nanoparticles (MONPs) consist of metal atoms bonded to oxygen [166,167]. These materials exhibit unique optical, electrical, thermal, magnetic, and biological properties, making them highly valuable across disciplines such as physics, chemistry, biology, biomedical engineering, and pharmaceutical sciences [165,168].
Organic NPs are derived from biological or synthetic substances such as proteins, carbohydrates, lipids, and polymers (e.g., chitosan, cellulose, and proteins). Common types include liposomes, micelles, dendrimers, and protein-based complexes like ferritin. Generally biodegradable and non-toxic, many of these NPs feature hollow cores, such as in liposomes, allowing for encapsulation of active compounds. While they are sensitive to environmental factors like heat and light, their surface functionality, physicochemical stability, and loading capacity make them ideal candidates for biomedical applications, including targeted drug delivery and cancer therapy [165,169].
Carbon-based NPs are composed entirely of carbon and encompass structures such as fullerenes, graphene, carbon nanotubes, carbon nanofibers, carbon black, and occasionally nanoscale activated carbon [170]. These materials are valued for their electrical conductivity, mechanical strength, electron affinity, and sorption capacity. They find application in diverse fields such as drug delivery, energy storage, bioimaging, photovoltaics, environmental sensing, and microbial detection. Emerging carbon nanostructures, including nanodiamonds and carbon nano-onions, demonstrate low toxicity and high biocompatibility, which supports their expanding role in drug delivery and tissue engineering [165]. Globally, over 232 nanotechnology-enabled products, developed by 75 companies in 26 countries, have been identified in the food and agriculture sectors [171].
Toxigenic fungi and mycotoxin contamination of food impact multiple agriculture (crop losses due to fungal infections and mycotoxin accumulation), the economy, the food industry (contamination of stored grains, nuts, dairy products, etc.), and medicine (mycotoxicosis and opportunistic fungal infections often resistant to standard antifungal treatments). While nanomaterials offer promise as antifungal delivery systems to control toxigenic fungi and mycotoxins in food [169], their application must remain simple, effective, sustainable, and devoid of health hazards. Prior research has primarily centered on engineered MNPs that exhibit intrinsic antifungal properties [134,135,172].
Other nanomaterials hold promise as antifungal systems in food, albeit with less extensive study than MNPs. Examples include the polymeric NPs (e.g., biodegradable polymers like chitosan for controlled release that protect antifungal compounds) [173]; nanoemulsions [174]; solid lipid nanoparticles (lipid-based carriers that improve drug stability and bioavailability) [175]; nanogels (hydrophilic networks that can encapsulate both hydrophilic and hydrophobic antifungal agents) [176]; liposomes (phospholipid vesicles that encapsulate antifungals for targeted delivery); biocompatible lipid vesicles that increase drug solubility and reduce toxicity [177]; cyclodextrin inclusion complexes (that heighten solubility and slow release) [178]; and dendrimers (branched nanostructures offering high drug loading capability and targeted delivery) [179].
The use of MNPs enhances antifungal activity and reduces mycotoxin contamination through several (1) increasing the solubility and bioavailability of antifungal agents; (2) allowing for the sustained release of compounds; (3) protecting molecules from degradation; (4) effectively targeting fungi; and (5) reducing dosages and side effects, thereby minimizing toxicity and environmental impact [88,158,169,172,180,181,182,183]. MNPs have garnered significant attention as novel antimicrobial agents. Researchers are currently investigating their effectiveness against toxigenic fungi and mycotoxins. This research aims to evaluate their potential as a strategy for addressing these challenges [120,172,184,185,186].
Engineered metal- and metal oxide-based NPs (MNPs and MONPs, respectively) are primarily inorganic NPs that can help combat antibiotic resistance [187]. MNPs are synthesized using both “top-down” and “bottom-up” approaches. The most commonly used metals include silver (Ag), copper (Cu), zinc (Zn), gold (Au), aluminum (Al), lead (Pb), cadmium (Cd), cobalt (Co), and iron (Fe). MONPs modify the properties of MNPs to enhance their reactivity and efficacy. Common metal oxides include copper oxide (CuO), zinc oxide (ZnO), iron oxide (Fe2O3), aluminum oxide (Al2O3), cerium oxide (CeO2), magnetite (Fe3O4), titanium dioxide (TiO2), and silicon dioxide (SiO2).
NPs may exhibit superior properties compared to their metal counterparts [126,170]. In addition to the formulation process, the resulting size and shape of NPs are crucial to their activity. NPs possess unique characteristics, including increased surface area, pore size, and charge density on their surfaces, all of which contribute to their distinctive properties. Moreover, NPs can exhibit a variety of shapes, colors, crystalline and amorphous structures, and sensitivity to environmental conditions [168,188]. Size is often one of the most critical factors to consider. Studies have demonstrated that smaller NPs tend to exhibit stronger antifungal properties compared to larger NPs, which can be attributed to their higher surface-area-to-volume ratio. This enhanced ratio improves binding at various target sites, facilitates diffusion, and reduces the aggregation propensity [126,185,189,190]. Currently, the prevention and control of fungal contamination using nanotechnology is a focal point of numerous studies. Despite significant advancements in this area of research, the development of antifungal nanoadditives for food-related systems remains in its early stages. In the agri-food sector, MNPs and MONPs have emerged as the most prevalent types of nanoparticles. The mechanisms of action of these agents differ significantly from those of traditional antibiotics, as they target multiple biomolecules, thereby hindering the development of resistant strains. Additionally, they exhibit activity against fungi that have already developed resistance [191]. In the field of agriculture, the extensive use of nanomaterials, particularly Ag, Cu, and Zn-based nanoformulations, has been adopted to enhance crop productivity and health. These nanomaterials are utilized as nanofertilizers and protect against toxigenic fungi and other harmful organisms [140,141,192,193,194]. However, the absence of science-based regulatory frameworks hinders the effective regulation of their use [142,195].
As said before, there are two approaches, named ‘top-down’ and ‘bottom-up’ methods, that are primarily utilized for the synthesis of MNPs (Figure 2).
Top-down methods commence with bulk quantities of materials that are subsequently reduced in size and combined with clusters of atoms or ions. Some top-down approaches utilize physical technologies that employ thermal energy, high-energy radiation, and mechanical pressure to facilitate processes such as material condensation, evaporation, abrasion, or melting. These techniques present several advantages over chemical methods, particularly in terms of minimizing solvent contamination in thin films and enhancing the uniformity of NP distribution. Below are some of the more commonly used physical methods.
High-energy ball milling is a mechanical technique that reduces bulk metal powders into NPs through intense collisions within a ball mill. This cost-effective and scalable method is widely employed for producing nanocomposites and metal alloys. However, challenges such as controlling particle size and preventing contamination persist. The process involves transferring kinetic energy from the grinding media, typically steel or tungsten carbide balls, to the material. These collisions, along with friction between the balls, the material, and the walls of the mill, generate significant energy, elevating both temperature and pressure within the mill. This energy facilitates the formation of fine powders, with the balls continuously interacting with the evolving particles. Exothermic reactions may occur during milling, producing additional heat and promoting NP formation. Milling devices include planetary, attrition, horizontal, vibrating, low-energy tumbling, and high-energy ball mills [188,196]. Figure 3 illustrates a schematic of a ball mill.
The energy transferred to the powder is influenced by several factors, including the type of mill used, the characteristics of the powder, milling speed, the size and size distribution of the balls, whether the milling is conducted in dry or wet conditions, milling temperature, and milling duration [197]. This method is particularly favored for the synthesis of intermetallic NPs [188]. It has been successfully applied to produce uniform ZnONPs with sizes ranging from 10 to 30 nm. The process operates at ambient temperature and is a straightforward, cost-effective, and solvent-free technique for generating ZnONPs under dry conditions [198]. Moreover, ball milling has proven to be an effective method for synthesizing biochar Ag/MnO nanocomposites [199].
This technique synthesizes MNPs by vaporizing a solid metal using high-energy laser pulses. It is most effective when conducted in a liquid medium, a process known as Laser Ablation Synthesis in Solution (LASiS). This method is considered “green” because it does not utilize toxic chemical precursors. In LASiS, a pulsed laser beam is focused on a metal target immersed in a liquid. The temperature at the irradiated spot rapidly increases, vaporizing the material and producing a laser-induced plasma plume composed of atoms, ions, electrons, and clusters that expand into the surrounding liquid. The plasma cools and condenses quickly, leading to the formation of clusters and NPs (Figure 4).
Laser ablation can be used to produce various types of NPs. The rapid quenching of vapor facilitates the generation of high-purity NPs within the quantum size range (<10 nm) [200]. The neodymium-doped yttrium aluminum garnet (Nd:YAG) laser operates at different wavelengths (1064, 532, 355, and 266 nm), which can influence the size and distribution of the NPs. Specifically, the 1064 nm wavelength results in larger NPs, while the shorter ultraviolet (UV) wavelengths yield smaller NPs with a narrower size distribution [201].
LASiS can be performed in different liquid media (water, acids, alkalis, organic solvents), targeting materials such as metals, metal alloys, and metal oxides. Water is the most commonly used solvent. The size and morphology of the NPs are significantly influenced by the temperature of the liquid medium. This method produces highly pure materials quickly, is free from contaminants, and is environmentally friendly, as it typically employs mild surfactants in the solvent [202]. However, LASiS can be expensive and energy-intensive, has a low production rate, and may encounter challenges in achieving precise control over NP size. The sizes of NPs can vary based on the type of NP and the experimental conditions, including both the laser source and the liquid medium.
The diversity of NPs generated through laser ablation is greater than that produced by other methods [196]. Laser ablation is a rapid and efficient technique for the production of AgNPs and can be synergistically combined with ball milling methods to enhance AgNP synthesis, while also creating opportunities for the development of novel nanocomposites and functional materials [203].
Sputtering is a type of physical vapor deposition (PVD) method used for the growth of thin films. In this process, a high electric field is generated within a chamber, causing high-energy ions to bombard a metal target, which serves as the cathode in a plasma environment. This bombardment results in the ejection of atoms from the cathode, which subsequently deposit onto a substrate (the anode), forming NPs, primarily MNPs and MONPs [204,205]. A noble gas, typically argon (Ar), is introduced into the chamber at low pressure. When the electric field is applied, electrons are accelerated and collide with the Ar atoms, generating argon ions (Ar^+^) and releasing additional electrons. This process produces a plasma, and the Ar^+^ ions within the plasma are attracted to the cathode (the target) due to the electric field (Figure 5).
There are various types of sputtering techniques, including direct current (DC) sputtering, radio frequency (RF) sputtering, magnetron sputtering, and reactive sputtering. The first method employs a constant DC voltage to generate plasma, making it suitable for the deposition of conductive materials such as metals. In magnetron sputtering, a magnetic field confines electrons near the target surface, thereby enhancing ionization and deposition efficiency. The second method utilizes an alternating current (AC) at radio frequencies (RFs) to sustain the plasma, enabling the deposition of both conductive and insulating materials, albeit at lower rates compared to the DC method.
DC sputtering can be enhanced through magnetron technology to improve deposition efficiency and film quality. The selection of this method depends on the specific material requirements and the desired properties of the film [206]. The magnetron sputtering deposition technique utilizes magnetic fields beneath the target to confine electrons in the plasma near the target. This confinement increases the likelihood of ionizing collisions, thereby enhancing plasma density and sputtering effectiveness. Cooling water is employed to prevent excessive heating of the target. In the reactive sputtering process, additional gases, such as O2, are introduced into the chamber to facilitate the formation of oxides. Traditional methods use solid substrates, but emerging approaches involve sputtering onto liquids, where the substrate is replaced by a low-vapor-pressure liquid (such as silicone oil, ionic liquids, or polymers) [205]. The inherent properties of ionic liquids or polymers render them ideal for stabilizing the resulting NPs. This method allows for enhanced control over size, morphology, and composition. The liquid medium facilitates nucleation and growth, ultimately yielding stable colloidal solutions. This technique has been successfully applied to the preparation of AgNPs and CuNPs. Strong capping agents and functionalized liquids have enabled the production of NPs approximately 2 nm in diameter [204,205,206,207,208]. Sputtering onto liquids offers a green and versatile approach, enabling the synthesis of pure NPs with precise size and shape control.
Spray pyrolysis (SP) entails atomizing a precursor metal-salt solution or suspension into micron-size aerosol droplets, which are transported by a carrier gas into a high-temperature furnace or heated environment, such as a flame, where solvent evaporation, solute precipitation, drying, and thermal decomposition occur. This sequence results in the formation of MNPs or MONPs, which are subsequently collected on a substrate (Figure 6).
Sometimes, additional heat treatment is required to optimize the crystallinity or morphology of the NPs [209]. The precursor solutions can be aqueous or organic and typically contain inorganic or metal–organic salts (e.g., chlorides, nitrates, carbonates), selected according to the desired final product [208,210,211]. Organic additives are often incorporated into the precursor solution to modify its properties or to influence the process, facilitating the formation of various nanostructures [209,212]. SP is considered a promising method for producing NPs with tailored characteristics. It is simple, cost-effective, and readily adaptable for industrial-scale production. Moreover, SP enables the synthesis of a broad range of nanomaterials, including metals, in a single step [213].
In ultrasonic SP, ultrasonic waves are applied to the precursor solution to generate micron-sized droplets. This technique is more efficient in terms of cost and operational stability compared to pneumatic and electrostatic nebulizers. However, it offers relatively low yield and is not suitable for high-viscosity liquids [209]. SP has been used to synthesize ZnONPs [214,215,216]. In another study, researchers used a pneumatic high-performance nebulizer with a methanolic solution of Zn(NO3)2 and a heating chamber maintained at 600–1000 °C to produce ZnO particles. The particle sizes obtained were 200 nm at 600 °C, 320 nm at 800 °C, and 400 nm at 1000 °C. The corresponding agglomerate sizes were 1.0 μm, 1.7 μm, and 2.3 μm, respectively [217].
Electrospray entails applying a high voltage to a polymeric solution containing metal precursors, which is delivered by a syringe pump through a nozzle. A positively charged jet forms at the needle tip, where surface tension maintains a hemispherical droplet shape while Coulombic repulsion promotes droplet detachment. As charge builds, the droplet deforms into the characteristic Taylor cone, from which an aerosol of charged droplets is emitted and directed toward a grounded collector near the cathode. During travel, solvent evaporation occurs, resulting in NP deposition on the collector [218,219] (Figure 7).
This technique enables the fabrication of monodisperse NPs and offers small particle size, efficient drug encapsulation, high drug loading, controlled surface properties, multi-layer NP formation in a single step, rapid production, high purity, and broad material versatility. The design of the metal collector significantly influences the deposition pattern and alignment of the particles, thereby shaping their final morphology. Diverse NP architectures, including spherical, core–shell, hollow, cup-shaped, and porous morphologies, can be produced [220].
Physical synthesis methods offer advantages such as rapid processing, use of radiation (e.g., ionizing or microwave) as a reducing agent, and the absence of hazardous chemicals. However, these methods generally suffer from low yield, high energy consumption, and non-uniform particle distribution [221].
In the bottom-up approach, nanostructures form via the sequential assembly of atoms or supersaturation induces nucleation, followed by cluster growth and eventual NP formation [222]. This strategy encompasses a range of methodologies, including physical, chemical/electrochemical, and biological processes. A critical evaluation of the available methods reveals that each possesses a distinct set of advantages and drawbacks, with each offering its advantages and drawbacks.
PVD is a broad class of vacuum deposition techniques used to produce thin films and NPs by physically transferring material from a source to a substrate in vapor form. Material is deposited onto a substrate, resulting in thin films or nanostructures. It includes several sub-techniques (e.g., thermal evaporation, electron- or ion-beam evaporation, sputtering, pulsed laser deposition, and arc vapor deposition). Depending on how NP synthesis is carried out, sputtering can be classified as either a bottom-up or a top-down process.
Evaporation/condensation of metal vapor is a subclass of PVD, also known as inert gas condensation. This method involves heating bulk pure metal to evaporate it into atoms, creating an aerosol within an inert gas atmosphere (He or Ar), followed by condensing the vapor into MNPs on a collector. This approach is considered a hybrid of top-down and bottom-up methodologies.
The PVD technique was applied in the preparation of CuNPs using an arc furnace at 5000 K to perform first the melting of the solid material and then the evaporation in an inert atmosphere made of a current of Ar as a carrier gas [223]. The CuNPs were in a size range from about 4 to 50 nm. The process has been applied to ZnNP synthesis [224]. The ZnNPs had a high purity (99.9%). However, the average particle size was found to be high (349 nm), which can be attributed to the evaporation temperature (approximately 900 °C). The synthesis of AgNPs in the size range of 9 to 32 nm has been accomplished [225]. This method uses pure metals, avoiding the need for chemical precursors and the presence of contaminants. The process parameters, evaporation temperature, and the inert gas flow significantly affect the particle mean size, size distribution, and shape.
Chemical methods include those where chemical reactions among substances are involved to produce NPs. Some chemical methods include the reduction of metal ions from salt solutions in the presence of reducing agents and capping substances. But there are other processes.
The sol–gel method involves the transition of a molecular precursor-based system from a liquid sol (typically colloidal) into a solid gel phase. It proceeds via chemical reactions such as hydrolysis or alcoholysis, using heating and stirring of molecular precursors (e.g., metal alkoxides) dissolved in water, alcohol, other organic solvents, or mixtures thereof, followed by condensation to form a colloidal suspension (sol), which then evolves into a three-dimensional gel network [226]. Subsequent drying and thermal treatment yield NPs. The properties of the dried gel depend critically on the drying thermal drying, supercritical drying, or freeze-drying produce xerogels, aerogels, or cryogels, respectively. This method has been demonstrated to be capable of synthesizing NPs exhibiting a range of structural and compositional features. It is effective for producing MONPs with high purity (>99.9%) and uniform sizes at relatively low temperatures (70–320 °C). This method is capable of producing two or more types of NPs simultaneously, meaning that alloy products are synthesized in one step by mixing two or more precursors of metal or metal oxide in certain ratios [226]. Metal oxide NPs, such as ZnONPs, have been synthesized by this process. These NPs can be useful in different areas [227].
In chemical vapor deposition (CVD), gaseous precursors undergo chemical reactions on a heated substrate, resulting in the deposition of a solid material, including MNPs. CVD may be viewed as a hybrid approach blending bottom-up and top-down features. Among the various CVD types, the most used are metal–organic CVD (MOCVD), microwave CVD (MWCVD) [228], and hot-wire CVD (HWCVD) [229].
The MOCVD process involves depositing a solid material following three consecutive (a) introduction of the volatile precursor by the carrier gas into a heated reactor chamber; (b) diffusion and adsorption of precursor vapors on the heated substrate surface and the formation of intermediate products; and (c) decomposition of these products on the heated substrate followed by nucleation and growth of the solid layer/grains, the formation of volatile by-products, and their removal by the carrier gas [230] (Figure 8). The adsorbed atoms form a solid phase that is deposited onto the substrate. They can also grow and nucleate, producing NPs. MOCVD has been utilized in the fabrication of AgNPs.
MWCVD uses microwaves to heat the chamber. The primary factors influencing the metal deposition process include the temperature and the pressure within the chamber, in addition to the nature of the precursors [231].
This technique bears a resemblance to MOCVD, yet it also exhibits notable distinctions. ALD is a cyclic process that utilizes alternating pulses of two or more gaseous precursors. These precursors are chemisorbed onto the substrate surface, thereby forming a film. This process also results in the removal of undesirable reaction by-products. The precursor pulses are separated by inert gas purges, which facilitate the removal of reaction byproducts and the suppression of unwanted gas-phase or pre-reactions. A diverse array of materials has been deposited using ALD, including nitrides, oxides, and certain metals. AgNP films have been deposited using direct liquid injection ALD with hexafluoroacetylacetone, silver(I), (1,5-cyclooctadiene), and propan-1-ol at a temperature between 123 and 128 °C [232].
Other chemical bottom-up approaches for NP synthesis include polyol methods, hydrothermal methods, co-precipitation methods, and microemulsion techniques [227].
This method encompasses the use of an electrochemical cell to perform the reduction of metal ions to atoms. The apparatus typically includes an anode made of the metal target, a cathode (which can be made of glassy carbon or platinum), and an electrolyte solution containing the metal ions. Several factors influence the size and morphology of the MNPs, including the nature of the anode and cathode, the electrolyte, the temperature, and the voltage and current employed in the process [233]. Capping agents may be added to help aggregation control. This process has been used to synthesize AgNPs [233,234] and CuNPs [235] among others.
Reduction may occur from the metal ions in a liquid solution when they are mixed with a suitable reagent that acts as a reducing agent. Usually, other substances that act as capping agents for the MNPs are also added. This method makes it possible to obtain MNPs both on the substrate surface and in the form of dispersed particles in colloidal systems, glasses, or polymers [230].
In the case of AgNPs, the salt commonly used is AgNO3, which readily dissolves in water. The reducing substances in question may be chemical compounds such as sodium borohydride (NaBH4) alone [236,237], which functions as both a reducing and a stabilizing agent. However, NaBH4 has been utilized in conjunction with other reagents in aqueous or organic solvents, including sodium dodecyl sulfate, chitosan, polyvinylpyrrolidone, trisodium citrate, dimethylformamide, and Tween 20 [238,239,240], among others. These reagents are typically dissolved in either an aqueous medium or an organic solvent. The reduction process transforms metal ions into metal atoms, and the citrate molecules cap the AgNPs, thereby preventing aggregation and promoting stability. The pH level is modulated through the incorporation of appropriate bases, such as ammonia, into the solution. In certain instances, the application of heat and agitation has been employed as a means to enhance the reduction of metal ions. A dark brown colloidal suspension of AgNPs is obtained. The suspension is then subjected to a process of centrifugation and water rinsing, a technique employed to eliminate the superfluous reagents and substances that are byproducts of the reaction. The NPs are then stored until use. In alternative processes, the reaction mixture is maintained at a low temperature in an ice bath to reduce the reaction rate and enhance the reproducibility of the process [240].
Biological synthesis is the process of reducing metal ions by utilizing natural specimens, such as extracts from terrestrial plant parts (e.g., leaves, fruits, roots, rhizomes, whole plants), bacteria, fungi, yeasts, algae, or honey. These extracts are also employed to cap and modify the surface of the synthesized NPs [241]. These procedures are the most cost-effective and environmentally friendly methods, known as “green synthesis” or biosynthesis, and are the subject of most publications on MNPs [223,242,243,244,245,246]. Many types of MNPs and MONPs have been synthesized; however, in the context of the present review, we are mainly interested in those made of Ag, Cu, Fe, CuO, Fe3O4, MgO, and ZnO [247]. A schematic of the generalized procedures to prepare MNPs through green synthesis is shown in Figure 9.
The organic material from biological species acts as a capping and stabilizing agent for the produced MNPs or MONPs. Among the fungi used to make extracts to reduce the solutions of metal salts, it is noteworthy to mention species of Fusarium, Penicillium, Aspergillus, or Talaromyces.
The pH and temperature affect the size and texture of the NPs produced using green technology. Therefore, regulating the pH and temperature of the solution media can control the NP size. Higher temperatures result in faster synthesis. NP production increases with size, which is also temperature-regulated [248]. Green synthesis has certain advantages compared to chemical and physical it is claimed to be non-toxic, pollution-free, environmentally friendly, economical, and more sustainable [249].
Thus, green-synthesized NPs are attractive for many localized or specific applications such as eco-friendly antimicrobials, certain medical uses, or applications in developing countries. However, their general usage on a global industrial scale is limited by batch-to-batch variability (inconsistent size, shape, and purity), unpredictable surface chemistry, and a lack of standard protocols. They are often application-specific rather than universally applicable.
A significant number of studies have investigated this domain of nanotechnology; however, the mechanisms of action involved in MNPs and MONPs used as antifungal agents are not fully elucidated. The ideal nano-fungicide would demonstrate equivalent or superior activity compared to that of the bulk metal at relatively lower concentrations. As illustrated in Figure 10, at the cellular level, MNPs have been observed to show a variety of effects. The antifungal activity of MNPs can be attributed to the following (a)The fungal cell wall undergoes changes and damage, including surface shrinkage, cell aggregation, pit and pore formation, and general deformation. Internalization of the NPs into fungal cells occurs through three principal (i) direct penetration of NPs through the cell wall, (ii) specific receptor-mediated adsorption followed by internalization, and (iii) uptake through ion transport proteins. During adsorption, NPs can embed within fungal cell walls, which induces morphological and functional changes [250]. Additionally, the NPs can release metal ions from the extracellular space. These ions can enter the fungal cell, thereby disrupting its biological processes [191].(b)The metal ions will contribute to the formation of NPs intracellularly through reduction processes by cellular organic compounds [251]. The fungal cell wall plays a critical role in various processes, including fungal growth and defense, morphogenesis, and biofilm formation. The primary functions of the cell include buffering fluctuations in osmotic pressure, sensing external stimuli, and protecting against detrimental conditions such as dryness, heat, and toxic molecules. The cell wall plays a pivotal role in the pathogenicity and virulence of pathogenic fungi, aiding in their invasion while protecting the fungus from host defense mechanisms [191]. The cell wall, a structural component of cells, appears to be a rigid structure; nevertheless, it is dynamic and is subject to constant remodeling due to several factors. These include fungal growth, which encompasses processes such as expansion, sporulation, and branching, as well as environmental challenges. The process of binary fission, also known as the expansion of hyphae, is contingent upon the concurrent activity of anabolic and catabolic enzymes. Therefore, based on the composition of the fungal cell wall, it can be concluded that the structure provides an optimal target for antifungal MNPs [191].(c)The disruption of the cell membrane is a consequence of the interaction between MNPs and the fungal cell membrane, leading to structural damage. As Slavin’s hypothesis states [191], positively charged metal-based NPs establish a robust bond with cell membranes, thereby increasing membrane permeability. This process facilitates the diffusion of essential ions and molecules, ultimately resulting in the demise of fungal cells.(d)The internal membranes are distorted, and there is an alteration in the organelle disposition. This phenomenon is evidenced by an increase in the intracellular vesicle and vacuole count and a decrease in cytoplasmic content. The loss of intracellular structure results in the accumulation of cytoplasm within the cell, accompanied by an apparent absence of organelles. This complicates the process of distinguishing between the cytoplasm, plasma membrane, and cell wall boundaries after exposure to NPs.(e)The underlying mechanism of this complication is the alteration of these structures by NPs, thereby obscuring the boundaries [185,190,251,252,253]. The generation of reactive oxygen species (ROS) is an inherent process within the human body. In the cell, the presence of metal ions or NPs has been observed to trigger the generation of ROS, which includes superoxide radicals and hydrogen peroxide. It has been demonstrated that ROS play a critical role in the antifungal activity mechanism of NPs. These substances have been demonstrated to induce oxidative stress in fungal cells. The oxidative stress can suppress the antioxidant defense mechanism of the fungus against ROS. Subsequently, these metal ions have been demonstrated to interact with cellular structures, thereby inducing damage to cellular components such as proteins, lipids, and DNA, which ultimately results in cell death [254,255].(f)Interaction with the fungal DNA is indicated herein. MNPs have been observed to penetrate fungal cells and interact with the DNA. The NPs can bind to the genetic material (which is negatively charged), resulting in structural damage, DNA fragmentation, or hindrance to DNA replication and transcription. This, in turn, disrupts the ability of the fungi to proliferate [191]. In addition, the NPs can induce mitochondrial DNA fragmentation, ribosome depolymerization, cellular dysfunction, and apoptosis [191]. The inhibition of enzyme activity is a consequence of the presence of MNPs within the fungal cell, thereby interfering with the function of the enzymes contained within. MNPs can bind to sulfhydryl groups on enzymes, thereby inhibiting their normal function and resulting in metabolic disruptions [118,256]. Metal ions have been observed to form strong coordination bonds with N, O, or S atoms. These atoms are found in abundance in organic compounds and biomolecules. Given the non-specific nature of the bond between metal ions and biomolecules, metal-based NPs typically demonstrate a broad spectrum of activities. It has been demonstrated that AgNPs exhibit reduced chemical reactivity in comparison to Ag^+^ ions. The interaction of Ag^+^ ions with a diverse array of biomolecules within the cell has been well documented, including nucleic acids, components of the cell wall, sulfhydryl groups of metabolic enzymes, and sulfur-containing cell components [257].(g)Synergistic effects. MNPs may exhibit enhanced antifungal activity when utilized in conjunction with other antifungal agents, suggesting a potential for synergistic interactions that can amplify the antifungal effect [258,259].
In soils, silver is predominantly found in the form of sulfides, often associated with iron, lead, or tellurides. It has been observed that this phenomenon is also connected with gold. The Ag^+^ ion is a prevalent constituent of surface waters, where it is present as sulfide, bicarbonate, or sulfate salts, or through adsorption onto organic or inorganic materials. Furthermore, the presence of Ag has been identified in conjunction with more complex ions, particularly in association with chlorides and sulfates. A considerable proportion of these forms demonstrate limited or sparingly soluble characteristics, thereby constraining their availability to biological organisms. Silver has gained a reputation for its biocidal properties [260]. It exhibits bactericidal, fungicidal, and virucidal properties irrespective of its form, including Ag^+^ ions, silver complexes, metallic silver (Ag^0^), and AgNPs. Due to their elevated biological activity, silver compounds are extensively utilized across a broad array of disciplines, particularly within the fields of biology and medicine. The elevated surface-to-volume ratio of AgNPs contributes to their enhanced biological efficacy in comparison to Ag^0^. Nonetheless, the reactivity of AgNPs is lower than that of Ag^+^ ions. These ions interact with a variety of biomolecules within a cell (e.g., nucleic acids, cell wall components, and sulfhydryl groups of metabolic enzymes) [261]. Consequently, the toxicity of the Ag^+^ ions is found to be higher than that of the AgNPs. It is noteworthy that AgNPs function as a source of silver ions. AgNPs exhibit a propensity for oxidative dissolution, a process that instigates the continuous release of Ag^+^ ions. The rate of Ag^+^ ion leaching from AgNPs is contingent upon external conditions and the physicochemical properties of the AgNPs [262].
Due to their proven efficacy in medical applications [263], the impact of AgNPs on various biological systems is currently under extensive research. This knowledge can contribute to the development of new methodologies in other scientific disciplines, including the control of fungal and mycotoxin contamination in food production. Some properties inherent to AgNPs must be taken into consideration when assessing their potential application in the domain of food technology. It has been established that smaller AgNPs exhibit heightened toxicity in comparison to their larger counterparts [186]. This phenomenon can be attributed primarily to the enhanced permeability of smaller AgNPs, which allows for easier penetration into cellular structures. In addition, smaller AgNPs demonstrate increased sensitivity to oxidative dissolution, leading to accelerated silver ion generation over larger AgNPs within shorter time frames [264]. The morphology of AgNP is a critical factor in regulating its biocidal characteristics. In many cases, molecules that regulate the morphology of the particles are deposited on the surface of the AgNPs. These molecules have also been demonstrated to exhibit biological activity. Consequently, the surface chemistry of AgNPs emerges as a pivotal factor in determining the biological activity of the entire system [265].
Therefore, in addition to size and shape, it is imperative to examine the role of chemicals utilized as reducing and stabilizing agents of AgNPs, as they significantly in-fluence the modeling of biological activity [266]. As demonstrated by Oćwieja and Barbasz [267], the type of reducing and stabilizing agents on AgNPs can amplify or re-duce the Ag+ ion release, or intensify or reduce the AgNP penetration through biological membranes. Therefore, the use of AgNP-stabilizing agents that possess biocidal proper-ties can cause synergistic effects, thus amplifying the silver toxicity [265]. Typically, AgNPs stabilized by inorganic anions exhibit a negative charge. Conversely, AgNPs en-veloped by organic compounds possessing moieties capable of protonation and depro-tonation can assume a negative or positive charge [267].
The surface charge of AgNPs has been demonstrated to influence the formation of a protein corona around NPs [268] and their subsequent interactions with the cell membrane [265,269]. It has been observed that the efficacy of different types of AgNPs, obtained by the reduction of silver ions with NaBH4 in the presence of trisodium citrate or cysteamine hydrochloride, varies when tested against Fusarium avenaceum and Fusarium equiseti [270]. The morphology of the two types of AgNPs was quasi-spherical. The citrate-stabilized AgNPs exhibited an average size of 15 ± 4 nm and were found to be negatively charged. In the context of this study, smaller cysteamine-capped AgNPs (12 ± 4 nm) were found to exhibit a positive surface charge and a higher silver ion release profile. It was observed that cysteamine-capped AgNPs caused damage to the conidia membranes and penetrated the cells of both fungal species, while citrate-stabilized AgNPs were deposited on their surface. A consensus emerged from the research that the cysteamine-capped AgNPs exhibited superior performance in comparison to the citrate-capped AgNPs. Consequently, ascertaining the precise chemical composition of the NP is imperative for its utilization in the domain of food technology. Despite the apparent popularity of plant extracts, bacteria, and fungi as reducing and stabilizing agents in the biosynthesis of AgNPs, this practice introduces uncertainty about the final composition of the NPs. This characteristic presents a notable disadvantage when considering their application in the food industry. Consequently, the employment of defined chemical compounds in the chemical synthesis of NPs may prove to be more advantageous than the utilization of complex reducing agents. The selective action of AgNPs against toxigenic fungi and mycotoxin production is highly desired; therefore, the design of AgNPs with selective antifungal activity and an acceptable size, shape, and charge to preserve the health of consumers and ecosystems in general is a priority objective for its possible implementation in food technology.
It has been documented that AgNPs exhibit a wide range of antimicrobial activity against various microorganisms [271]. The antimicrobial action of AgNPs has been reported on a variety of pathogens, including bacteria [240,272], fungi [191,270,273], and viruses [274]. Despite the paucity of research on the antifungal activity of MNPs on toxigenic fungi affecting crops in pre- and post-harvest, and their effect on mycotoxin biosynthesis, the existing literature on this subject is predominantly focused on AgNPs [172,238,275].
The impact of engineered AgNPs, produced through biological, chemical, and physical synthesis, as well as commercial formulations, has been examined concerning various fungal species classified as mycotoxin producers. However, the majority of these studies have focused exclusively on the impact of these NPs on the regulation of fungal growth.
Table 1 presents a compendium of recent publications that, to varying extents and with varying degrees of experimental rigor, examine the antifungal properties of AgNPs against species designated as mycotoxin producers. It is important to note that the utilization of these strains in the aforementioned studies does not inherently imply that they possess the characteristic of producing mycotoxins.
Table 2 enumerates the works in Table 1 where, in addition to the effect of AgNPs on fungal growth, the effects on mycotoxin production are also studied. Consequently, in such cases, these fungi were classified as mycotoxin-producing strains. These are the following studies [238,275,276,277,278,279,280,281,282,283,284,285].
As shown in Table 1 and Table 2, the majority of the examined AgNPs exhibit a spherical morphology, which may be attributed to the relative ease with which this shape can be synthesized. In terms of size, the focus of the majority of studies has been on suspensions of polydisperse AgNPs. This approach precludes the possibility of conducting a thorough investigation into the relationship between the size of the NPs and their antifungal activity. The studies illustrated in Table 1 and Table 2 exhibit a consistent pattern. The findings indicate that as the concentration of AgNPs increases, there is a concomitant decline in fungal growth, the number of viable spores, and the production of mycotoxins. This phenomenon occurs irrespective of other variables, including the synthesis method, the size and shape of the NPs, and the specific fungal species utilized in the testing. Furthermore, the emergence of resistant strains following the treatment regimen was not observed.
The most extensive works in which the antifungal and anti-mycotoxin effect of AgNPs are studied are those of Gómez et al. [238] and Tarazona et al. [275]. As reflected in Table 1 and Table 2, the assays were executed with AgNPs exhibiting an average size of 30.9 nm (range: 14–100 nm), and obtained through chemical synthesis. The study examined the effects of doses ranging from 2 to 45 ppm of AgNPs. The treatments entailed maintaining the fungal spores in contact with the AgNPs in a liquid medium under agitation for varying durations (2 to 30 h). After the treatments, a comprehensive analysis was conducted to assess several parameters, including spore viability, the spore germination lag phase, the growth rate (GR) of colonies produced by the treated spores, and mycotoxin production. These experiments were performed on a corn-based medium. The tested species included A. flavus, A. parasiticus, A. carbonarius, A. niger, A. ochraceus, A. westerdijkiae, A. steynii, Penicillium verrucosum, F. graminearum, F. culmorum, F. sporotrichioides, F. langsethiae, F. poae, F. oxysporum, F. proliferatum, and F. verticillioides. Concurrently, the impact of these AgNPs on the production of the primary mycotoxins associated with these species was aflatoxins (A. flavus and A. parasiticus), OTA (A. carbonarius, A. niger, A. ochraceus, A. westerdijkiae, A. steynii, Penicillium spp.), DON, 3-acetyldeoxynivalenol, ZEA (F. graminearum, F. culmorum), T-2 and HT-2 (F. sporotrichioides and F. langsethiae), NIV (F. poae), and FB1 and FB2 (F. verticillioides and F. proliferatum). The results demonstrated the significant antifungal properties of AgNPs against these species. Treatments involving extended AgNPs-spore contact times (30 h) resulted in the complete eradication of all exposed spores. In many cases, intermediate exposure times (4–20 h) yielded similar outcomes. Spores that survived the treatments exhibited a significant delay in the onset of germination and colony formation. Effective doses (EDs) to inhibit the number of viable spores to 50%, 90%, and 100% compared to untreated controls (ED50, ED90, and ED100) were in the range 2–45 ppm. The antifungal properties of AgNPs were influenced by various factors, including dosage, duration of exposure, the specific species of fungus, and the interaction between these factors. All these factors significantly influence spore viability, lag period, GR, and mycotoxin production. Work of this type is necessary because these toxigenic fungi and mycotoxins often coexist on the same substrate, and it is important to know the spectrum of antifungal and anti-mycotoxin action of the tested NPs to determine more precisely their possible effectiveness in practice. Other authors have described higher effective doses of NPs obtained by chemical synthesis. Thus, Sedaghati et al. [276] observed a decrease in mycelial mass of A. parasiticus of 92% in cultures treated with AgNP doses of 250 ppm, and Dananjaya et al. [315] observed a decrease of 81.52% in colonial growth of F. oxysporum using an AgNP dose of 1000 ppm.
The results described for AgNPs obtained by biological synthesis differ widely. Bocate et al. [288], using broth microdilution assays, incubated fungi at 30 °C for 48 h, found minimal inhibitory concentrations (MICs) for AgNPs of 8, 4, 8, 8, 4, and 8 ppm for A. flavus, A. melleus, A. nomius, A. ochraceus, and A. parasiticus, respectively, and minimal fungicidal concentrations (MFCs) of 64, 16, 32, 32, 16, and 32 ppm, respectively. However, Yassin et al. [316] studied the effect of AgNPs on A. flavus var. columnaris in potato dextrose agar (PDA) medium supplemented with AgNPs (size 3–13 nm); the cultures were incubated at 28 °C for 10 days, and colony diameters were measured daily. In these cultures, the ED50 and ED95 were 224.5 ppm and 4001.8 ppm, respectively. The effect of AgNPs on mycotoxin production was not studied in these reports.
The results reported in the literature for commercial AgNPs also vary (Table 1 and Table 2). Five ppm of AgNPs with a diameter of 5 nm and 2 ppm of AgNPs with a diameter of 0.65 nm inhibited the growth and spore germination of P. verrucosum, respectively [283]. It was also found that 5 ppm of AgNPs with a diameter of 5 nm inhibited OTA and CIT production. However, it has been documented that concentrations of 100 ppm of 7–25 nm AgNPs were necessary to inhibit the growth of A. alternata, F. oxysporum f. sp. cucumerinum, F. oxysporum f. sp. lycopersici, F. oxysporum, and F. solani in percentages ranging from 59.5% to 81.1% on PDA medium, 26.5% to 65.35% on malt extract agar (MEA) medium, and 76.5% to 81.2% on corn meal agar (CMA) medium [310]. The possible mycotoxins remaining in the medium were not determined.
The interpretation of the results reported in the literature regarding AgNP assays for the control of toxigenic fungi growth and mycotoxin production is not easy. Several factors influence this issue, primarily the discrepancies found in some reports concerning the application of microbiological and analytical chemistry methods in antifungal assays and in the determination of mycotoxins in in vitro cultures, along with their significant heterogeneity. Furthermore, the utilization of fungal strains classified as mycotoxin producers remains sporadic. Moreover, conducting a comparative analysis of the studies on the effectiveness of AgNPs in controlling the growth of toxigenic fungi and mycotoxin production is challenging. This is because each work employs different AgNPs (size, shape, type of synthesis, etc.), methodologies, culture conditions, and fungal species and strains. Standardized effective doses (EDs), such as the ED50, ED90, or ED100 of the AgNPs, fungal GR, etc. [238,275], which allow conclusions to be drawn, are rarely calculated. There are even different interpretations of the MIC concept [275,288,291,296].
Despite these limitations, the general conclusion that can be drawn from the trials performed so far is that AgNPs are very effective in controlling the growth of numerous species described as mycotoxin producers and do not induce resistance. This review also indicates that the antifungal and antimycotoxin effects of the AgNPs are similar; the absence or reduction of fungal growth is associated with the absence or reduction of mycotoxins in the medium. However, it has been detected that sublethal AgNP doses can stimulate DON production [186]. While this result is timely, further research is needed to understand the effects of AgNPs on the expression of genes involved in mycotoxin production under various environmental conditions. In addition, it will be essential to investigate the impact of AgNPs on fungal growth and mycotoxin production, as studies that address both of these factors simultaneously are limited.
Copper (Cu) is one of the most essential micronutrient metals/minerals required by living organisms (humans, animals, and plants) [317]. In adults, the average human body contains between 1.4 and 2.1 mg of Cu per kg of body weight (kg/bw). According to the World Health Organization (WHO), the recommended daily upper limit of Cu for adults is 2–3 mg. However, this small amount is essential to the overall well-being of humans. This element is crucial for growth and development, as well as the maturation of the nervous, bone, and other systems. It is also an essential component of enzymes that facilitate glucose, amino acids, and cholesterol metabolism, along with various catalytic reactions. As with other trace elements, Cu must be kept in equilibrium in the body. It is not synthesized in the body and thus must be obtained through dietary sources. The primary dietary sources of copper for humans and animals include three main seafood (e.g., oysters and other shellfish), organ meats (e.g., kidneys and liver), and dark leafy greens, whole grains, legumes (e.g., beans and lentils), nuts, potatoes, and dried fruits (e.g., prunes, cocoa, and black pepper). The use of Cu as a nutritional dietary supplement in animal feeds has been categorized as “generally recognized as safe” (GRAS) by both the US Food and Drug Administration (US FDA) and the European Food Safety Authority (EFSA) Panel on Additives and Products or Substances used in Animal Feed (FEEDAP Panel) [318]. For optimal plant growth and development, the concentration of Cu ranges between 0.05 and 0.5 ppm, with most tissues (e.g., vascular, dermal, and ground tissue cells) between 3 and 10 ppm [139]. Cu is involved in a variety of physiological processes, including the formation of chlorophyll and photosynthesis, as well as assisting in plant respiration and the metabolism of carbohydrates and proteins. Some of the enzymatic reactions use Cu as a cofactor, including the activation of metalloproteins and those involved in lignin synthesis [193]. The primary source of Cu for plants is fertilizers and several fungicides, which contain Cu as their active ingredient. The use of Cu is advantageous for several reasons. First, it is significantly more affordable than its counterpart, silver. Second, it is less toxic and highly available. Third, it has been reported to be effective against a variety of pathogenic and toxigenic fungi, including A. carbonarius, A. fumigatus, A. niger, Alternaria solani, and F. expansum [319,320].
Generally employed fungicides are not approved for use in organic agriculture. The use of Cu antifungal agents has resulted in a new option in this field. Cu is recognized as a potent antimicrobial metal with comprehensive control. Some copper is classified as a potent antimicrobial element with comprehensive control. Furthermore, some copper-based fungicides, which are divided into both inorganic and organic fungicides, are approved for organic farming practices [139,321]. Cu-based fungicides are categorized as Cu hydroxide fungicides, Cu oxychloride fungicides, and Cu oxide fungicides, and their application can be made through suspension concentrate, wettable powder, and water granules [193].
However, in both humans and animals, abnormal Cu metabolism or content has been associated with a multitude of diseases, including those associated with immune function deterioration, diabetes, coronary heart disease, and osteoporosis [322]. In agriculture, the consistent use and effectiveness of Cu fungicides pose several challenges. For instance, the accumulation of Cu in roots results in plant toxicity, which restricts root growth by burning the root tips and thereby causing excess lateral root growth. Additionally, the build-up of copper in sediments can lead to long-term soil contamination [320,323,324].
To address these challenges, there is a constant search for alternatives to optimize Cu fungicides with limited to no toxicity effects. Due to their cost-effectiveness, unique nanoscale properties, well-established antimicrobial activity, and broad-spectrum applicability, CuNPs are showing great potential in agricultural applications for pest management and disease control. Diverse commercial Cu nanoformulations are utilized in agriculture [193]. Copper-based NPs, such as CuNPs and CuONPs, are used frequently in nanoformulations and agrochemicals because of their ability to efficiently deliver and control the pesticide and fertilizer release. Other agricultural applications include the protection of plants, promotion of plant growth, the use of nanosensors, and the use of antifungal and antibacterial activities [194]. Synthesizing CuNPs presents a significant challenge due to the rapid oxidation of copper, which results in the formation of Cu2O, CuO, and Cu(OH)2. Consequently, there are various studies on the use of CuNPs and CuONPs against toxigenic fungi. The primary synthesis methods used to produce these metal NPs, as well as the assays employed to assess their efficacy against the specified mycotoxin-producing species and mycotoxin production, are outlined in Table 3, Table 4 and Table 5.
CuNPs and CuONPs have been studied less frequently than AgNPs, likely due to observations indicating their reduced effectiveness against toxigenic fungal species [285]. As with AgNPs, the literature on the antifungal and anti-mycotoxin effects of CuNPs or CuONPs contains a great deal of variation. This heterogeneity is seen in the methods for their synthesis, physicochemical characteristics, and the tests on their effectiveness against fungi and mycotoxin production (Table 3, Table 4 and Table 5). In reports, there is often a lack of information necessary for accurate reproduction of antifungal assays and comparative analysis.
As in the case of AgNPs, the CuNPs and CuONPs morphology is generally spherical, and their size ranges between 2 and 500 nm (Table 3, Table 4 and Table 5). The most commonly used antifungal activity assays are well diffusion methods, radial colony growth, and MIC determination. The size of growth inhibition halos, reduction percentage, total inhibition of the fungal colony growth, and MIC values also vary widely among reports. However, in all cases, CuNPs or CuONPs are effective as antifungal and anti-mycotoxin agents to a greater or lesser extent.
Among the studies shown in Table 3 and Table 5, the one by Pérez-de-León et al. [285] is noteworthy because it is the only one in which the effectiveness of CuNPs against fungal growth (in this case, F. verticillioides) and against mycotoxin production (in this case, FB1) is studied simultaneously. In this study, a comparative analysis of the effectiveness of CuNPs (2.5 ± 0.3 nm) and AgNPs (17 ± 1.5 nm) obtained in both cases by the same chemical reduction method and under the same conditions is also carried out. Results revealed that both these NPs exhibited significant antifungal activity against F. verticillioides, at 125 and 75 ppm for CuNPs and AgNPs, respectively. Regarding the control of FB1 production, the CuNPs completely inhibited FB1 production at levels ≥ 100 ppm (Table 5), while AgNPs suppressed FB1 production at levels ≥ 20 ppm (Table 2). The authors suggest that the activity of treatment with CuNPs and AgNPs occurred due to changes caused in the structure of the hyphae, such as the interference in mycelial growth, loss of contour and uniformity of the hyphae, and rupture of the hyphae, resulting in a significant reduction in FB1 biosynthesis. It is worth noting that although AgNPs perform better than CuNPs in controlling F. verticillioides and producing FB1, the major drawback of the CuNPs tested in [285] for their possible application in food preservation is that their size is excessively small, so that their toxicity to the consumer could be high. In other report [325], larger CuNPs (200–500 nm) also obtained by chemical synthesis are used against F. oxysporum f. sp. lycopersici with good results. However, as expected, the concentrations required for a significant reduction of fungal growth (80%) were 1000 ppm, while in [286], the MIC against F. verticillioides was 125 ppm.
As stated in another report [313], CuNPs between 26 and 40 nm, produced biologically from green and black tea extracts, were found to decrease aflatoxin (AF) production by 83.1 ± 2.9% at a concentration of 100 ppm for both A. flavus and A. parasiticus. Similarly, AgNPs, synthesized using the aforementioned method, exhibited a 100% reduction in AF production. In a similar study, extracts of Syzygium cumini leaves were used for synthesis [314]. The resulting CuNPs (28–35 nm) at a concentration of 100 ppm reduced AF production by 75.7 ± 3.2% (Table 5). Moreover, AgNPs obtained by the same method and at the same concentration inhibited AF biosynthesis (Table 2). Despite the higher antifungal and anti-mycotoxin effectiveness of AgNPs compared to CuNPs reported in these studies, CuNPs may be a more suitable choice for agricultural and food technology applications because Cu is an essential micronutrient for living organisms and promotes plant growth.
In summary, the responsible and sustainable use of Cu nanoformulations provides a noteworthy strategy to reduce the amount of Cu introduced into agroecosystems. This strategy effectively mitigates ecotoxicological risks while concurrently delivering substantial Cu for antifungal and micronutrient cofactor activities. These are vital for facilitating essential plant pathways. However, the use of Cu nanofungicides has proven to be more beneficial than conventional fungicides. Investing in understanding the ecotoxicology of the Cu nanoformulation lifecycle is crucial. The structural design of Cu nanofungicides has the capacity to influence the physicochemical, fungicidal, and fungistatic properties attributed to bioavailability and cupric (Cu^2+^) ion release as a function of antifungal activity and overall toxicity profile. To avert toxicity, it is important to consider green nanotechnologies and dosimetric calculations. This combination of green, sustainable nanotechnology enhances fungicidal activity, thereby eliminating the risk of mycotoxins. It will enhance crop and food productivity and management while avoiding ecotoxicological or phytotoxic effects in agroecosystems (crops, soil), animals, or humans.
Zinc (Zn) is an essential component of life; after iron, it is the second most abundant transition metal ion (Zn^2+^) in living organisms. Approximately 5–6% and 9–10% of proteins in prokaryotes and eukaryotes, respectively, are dependent on Zn for their biological functions. It is essential for cell growth and division, immune function, enzyme reactions, as well as DNA and protein synthesis. Zn has been shown to effectively reduce inflammation, boost immune health, reduce the risk of age-related diseases, and speed wound healing. Notably, more than 50% of Zn-binding proteins are enzymes. In most of these cases, the metal plays a catalytic role. Approximately 20% of them utilize Zn as a structural component, while a smaller percentage function as regulators or substrates for enzyme activity. The requirement for zinc (Zn) in such a large number of proteins illustrates its critical role in many biological processes. The essential nature of Zn for cell viability, along with its toxic nature at high levels, prompted the evolution of export and import systems among prokaryotes and eukaryotes to maintain ionic homeostasis [348,349]. Additionally, Zn plays a pivotal role as an intracellular second messenger, connecting environmental changes with the regulation of metabolic activity in root nodules [350]. Zn is a naturally occurring element that plays a significant role in the metabolism of humans, animals, and plants.
Among zinc nanomaterials, zinc oxide NPs (ZnONPs) have been the focus of extensive research due to their valuable properties, including biocompatibility, eco-friendliness, low toxicity, low cost, ease of fabrication, high photosensitivity, large excitation binding energy, high thermal conductivity, and stability under harsh environmental conditions [351,352,353]. According to Mirzaei and Darroudi [354], ZnO is widely regarded as an essential nutritional supplement. Due to these properties, ZnONPs are widely used in several fields, such as agriculture and food, with a focus on drought and salinity tolerance, antimicrobial properties, and fertilizers that enhance crop yield and quality, as well as food packaging [352,355,356,357,358]. The field of medicine also holds significant potential, particularly in the realm of biomedical applications, including anti-cancer treatments. The product has been shown to possess antimicrobial, antioxidant, anti-inflammatory, wound healing, and drug delivery properties [349,352,359]. In addition, it has been identified as an effective photocatalyst agent, offering a promising method for wastewater treatment [360,361,362,363]. The ZnONP applications also extend to other fields. Given this background, ZnONPs are currently considered the most promising antibiotic nanoscale agents due to their unique properties. ZnO has been officially recognized by the U.S. Food and Drug Administration (FDA) as safe for use in food production and has been registered under the designation GRAS indicated in section 21CFR182.899 [364]. According to the current scientific consensus, the use of ZnONPs poses no significant threat to public health [364].
According to the results reported in the literature, ZnONPs have been the most studied Zn particles against fungal species described as mycotoxin producers. ZnONPs obtained by chemical synthesis, biological synthesis, and commercial formulations have undergone rigorous testing to ensure their effectiveness and safety. These reports detail in vitro assays utilizing a diverse array of NPs, encompassing a range of sizes, shapes, and concentrations (see Table 6 for details).
Pariona et al. [365] tested different ZnO particles with three characteristic shapes and synthesized by colloidal and hydrothermal techniques. They were tested against F. oxysporum f. sp. lycopersici and F. solani. The particles tested included spheroidal particles (ZnONPs) with an average diameter of 18 ± 4 nm that were arranged in agglomerates. The other particles tested were platelet particles (ZnOPls) with an average diameter of around 246 ± 40 nm and an average thickness of 48 ± 6 nm. The third type of particle tested was elongated rod particles (ZnORds) with an average diameter of 786 ± 142 nm and an average length of 9330 ± 1500 nm. The results indicated that the antifungal activity depends on both the types of ZnO particles and the specific toxigenic fungal species involved.
The order of effectiveness of the three particles was ZnOPls > ZnONPs > ZnORds (Table 6). F. solani was more sensitive to the treatments than F. oxysporum. Furthermore, the growth morphology, color, texture, and density of the fungi were observed for each treatment. For instance, the color of the mycelium of F. oxysporum is determined by the levels of the three ZnO particles. This phenomenon can be attributed to the active defense mechanism against the high ROS generated by the ZnO treatments [365].
This defense mechanism has also been observed in F. oxysporum treated with different concentrations of copper nanoparticles obtained by green synthesis [334]. Furthermore, a change in the texture of the mycelium was observed in the two fungal species treated with high concentrations of zinc oxide (ZnO) (750 and 1000 ppm). The generated ROS stimulate this effect on the texture of the mycelium by interacting with fungal biomolecules and promoting their distortion. Changes in texture have also been documented for F. solani and F. oxysporum treated with CuNPs. The effectiveness of high concentrations of ZnONPs (47.2 nm diameter) obtained by chemical synthesis against toxigenic fungi has also been studied [335]. The effects of exposure to 5000 ppm ZnONPs were examined in two strains of Alternaria alternata and one strain of F. verticillioides [368]. The study found that exposure to the chemical resulted in growth inhibition halos measuring 30.63, 36.28, and 34.77 mm, respectively.
The antifungal properties of ZnO particles obtained through biological synthesis have also been thoroughly examined. According to Jayaseelan et al. [373], ZnONPs synthesized using Aeromonas hydrophila demonstrated significant antifungal activity against relevant mycotoxin-producing species, such as A. flavus and A. niger. Additionally, Rajiv et al. validated the antifungal activity of ZnONPs and found that it is size-dependent. The highest inhibition was reported against A. flavus and A. niger at 25 ppm. Furthermore, the antifungal activity of ZnONPs against five fungal plant pathogens, including A. alternata, A. niger, F. oxysporum, and P. expansum, was confirmed [375]. The lowest minimum inhibitory concentration, 16 ppm, was reported against A. niger. Additionally, ZnONPs synthesized using Serratia nematodiphila exhibited activity against Alternaria sp. [379].
The antifungal activity of commercial ZnO particles has been tested against various species of toxigenic fungi, including P. expansum [384,386], A. alternata [384,385], F. oxysporum [347,386,387], and A. solani [347] at different concentrations using various methods. The results summarized in Table 6 show that the inhibition of fungal growth depends on the characteristics of the NP, concentration, and fungal species. The highest percentages of inhibition were obtained with the ZnOPNs used in the [347] trials, where 1000 ppm of NPs produced 91.13% and 98.69% inhibition of F. oxysporum and A. solani growth, respectively, and in the [386] trials, where 12 ppm of NPs produced 77.5% and 100% inhibition of F. oxysporum and P. expansum growth, respectively.
In addition to its capacity to regulate the proliferation of toxigenic fungi, the primary application of ZnONPs pertains to the suppression of mycotoxin synthesis. However, this aspect has received scant scholarly attention (Table 7). Savi et al. [366] investigated the inhibitory effect of ZnONPs at a 100 mM concentration on DON, AFB1, and CIT production in cultures of F. graminearum, A. flavus, and P. citrinum, respectively. The percentages of inhibition of the biosynthesis of these mycotoxins were 100% for DON and over 60% and 5% for AFs and CIT, respectively. Hassan et al. [370] found that the growth of A. flavus and AF production were inhibited by the addition of 8 ppm of ZnONPs. These inhibitory results were also observed for both A. ochraceus and OTA and A. niger and FB2 production when the concentration of ZnONPs was increased to 10 ppm. Tests with commercial ZnOPNs at a concentration of 12 ppm have demonstrated inhibition of fusaric acid production by F. oxysporum and patulin production by P. expansum by 99.5% and 92.26%, respectively. The findings indicated that the presence of ZnONPs within a food matrix may impede the proliferation of deleterious fungi and concomitantly curtail the synthesis of mycotoxins by toxigenic fungi.
Research on the effect of metal oxide nanoparticles other than CuONPs and ZnONPs on toxigenic fungi and mycotoxin production is very scarce. Some studies have been conducted on the effectiveness of Fe2O3NPs [347,388] or MgONPs [369] in combating certain species of toxigenic fungi.
Iron (Fe) is a prevalent element in the human body, where it is found in various prosthetic groups, such as iron-sulfur clusters and heme, a complex of iron and protoporphyrin, or coordinated with oxygen in iron-containing enzymes. Fe is involved in different biological processes, including energy production, O2 transport, deoxyribonucleotide production, and replication and repair of the DNA. The regulatory framework under consideration is predicated on the premise that intestinal Fe absorption is of pivotal significance. This process is subject to the concerted influence of numerous proteins, including, but not limited to, divalent metal transporter 1, ferroportin, transferrin, and transferrin receptors. Ferroxidases, including duodenal cytochrome B, ceruloplasmin, and hephaestin, are coordinately regulated by hepcidin to ensure efficient acquisition and utilization of iron. Acute hypoferremia can affect other cells and tissues owing to the decreased synthesis of iron-containing enzymes, which are critical for cell function. Conversely, the chemical reactivity of iron contributes to its potential toxicity. Therefore, it is imperative to maintain precise balance in Fe metabolism to ensure optimal human well-being, necessitating regulation at multiple levels [389,390].
Magnesium (Mg) has been determined to be the fourth most abundant metallic element within the human body. As demonstrated in numerous studies, Mg has been shown to serve as a cofactor for over 300 enzymes, thus modulating a variety of essential physiological processes. These processes include, but are not limited to, muscle contraction, neuromuscular conduction, glycemic control, myocardial contraction, and blood pressure regulation. In addition, Mg plays a pivotal role in various physiological processes, including energy production, active transmembrane transport for other ions, the synthesis of nuclear materials, and bone development. This element has been demonstrated to play an instrumental role in the therapeutic and preventive management of a wide range of medical conditions, including but not limited to diabetes, osteoporosis, bronchial asthma, migraine, and cardiovascular illnesses [391].
Tests have been conducted using the agar diffusion method with Fe2O3NPs (10–30 nm) against P. chrysogenum, A. alternata, and A. niger. The results showed that 500 ppm of NPs could induce growth inhibition halos of 28.67 ± 1.53 mm, 21.33 ± 3.83 mm, and 26.33 ± 1.15 mm, respectively [388]. However, Vera-Reyes et al. [347] tested commercial Fe2O3NPs (30 nm in diameter) against F. oxysporum and A. solani at concentrations ranging from 100 to 1000 ppm. The efficacy of these NPs in reducing colony growth was negligible or minimal in comparison to ZnONPs or CuONPs, which, at 1000 ppm, resulted in a colony growth reduction of 99% and 95%, respectively. Similarly, a decline in A. alternata and F. oxysporum spore germination of 66.28 to 12.96% has been documented through the utilization of MgONPs (~50 ± 10 nm) [369]. Given the critical role of Fe and Mg in sustaining optimal organismal function, further investigation of these NPs against toxigenic fungi on a broad scale is imperative. Such research is crucial to comprehensively assess their efficacy and determine their potential to counteract toxigenic fungi and mycotoxins in food systems.
In summary, as outlined in Figure 11, this review paper presents a comprehensive list of the predominant species of toxigenic fungi against which various NP types, including AgNPs, CuNPs, CuONPs, CuONPs, ZnONPs, Fe2O3NPs, and MgONPs, have been tested. As illustrated in Figure 12, certain NPs have been observed to inhibit the production of various mycotoxins, either completely or partially.
The extant research on the effect of MNPs and MONPs against the described mycotoxin-producing species and their consequences on the mycotoxin production by these fungi indicates that they can be excellent tools in the management of these risks in food. However, further research is required before their potential application in practice can be determined.
The issue of food sustainability and safety is a significant challenge faced by developing countries due to the expanding human population. The application of nanotechnology offers a straightforward, viable, and dependable solution to these challenges. Advances in nanotechnology have the potential to provide a variety of solutions to issues related to food, its storage, and shelf life, thus offering sustainable economic, commercial, and health benefits. Despite the demonstrated potential of MNPs and MONPs in a variety of applications within the food industry, significant limitations and knowledge gaps persist. In this review, we demonstrate that MNPs (AgNPs, CuNPs) and MONPs (CuONPs, ZnONPs, Fe2O3NPs, Fe3O4NPs, MgONPs) possess remarkable antifungal properties and can contribute to the prevention of contamination and the development of toxigenic fungi and mycotoxin production. These properties may offer significant benefits in food processing environments and in food itself. However, the implementation of these systems in the food industry is subject to specific regulatory frameworks and requires rigorous safety assessments before integration. Within the European Union, the utilization of nanomaterials in food is subject to a series of regulatory frameworks. According to Regulation (EU) 10/2011, the utilization of nanoform substances in food contact materials is permissible under the condition that they have been granted approval by the European Food Safety Authority (EFSA) following a comprehensive case-by-case evaluation. According to Regulation (EU) 1169/2011, all ingredients present in the form of engineered nanomaterials must be explicitly indicated in the list of ingredients, accompanied by the term “nano” in brackets. Regulation (EU) 2015/2283 [164] stipulates that any food containing or consisting of engineered nanomaterials should be classified as a novel food and undergo a rigorous evaluation before its placement on the market. Furthermore, there are concerns regarding the safety and toxicity of MNPs, particularly concerning their direct introduction into food or their potential migration into food from packaging, paints, and coatings [392,393]. Consequently, it is imperative to conduct thorough toxicological studies and adhere to current regulations before implementation in the food industry.
According to an analysis of the relevant literature, the most active area of development for engineered MNPs and MONPs, as promising nanoadditives, is in the fabrication and improvement of food packaging, paints, and coatings with antifungal properties used in the food industry [394]. This may be due to the public’s concerns regarding “nanofoods,” stemming from the uncertainties surrounding the safety of nanomaterials. Consumers are more willing to embrace nanomaterials in “out-of-food” uses than those where NPs are applied to food directly [395]. The use of MNPs or MONPs for food packaging is a rapidly growing area. Ag, Cu, CuO, and ZnO are examples of such NPs. These materials are chemically stable and characterized by an elevated aspect ratio. This review demonstrates that these NPs exhibit remarkable antifungal properties against toxigenic fungi, resulting in their growth inhibition. Consequently, they are exceptionally useful for creating innovative active materials in the biomedical and food technology sectors. It is important to note that some of the metallic constituents found in NPs are vital minerals for human physiology [348,349,389,390]. Current market demands are no longer met by traditional packaging methods. This has created a demand for more advanced and innovative approaches to food packaging. The development of novel food packaging systems has been driven by evolving market demands, including consumer preferences for “health-conscious” and high-quality food items, as well as the imperative to reduce the adverse environmental footprint of food packaging. MNPs (e.g., AgNPs, CuNPs) and MONPs (e.g., CuONPs, ZnONPs, Fe2O3NPs, Fe3O4NPs, MgONPs) are being actively explored in the food industry, especially in the manufacture of bioactive packaging [396]. Please refer to the works of Zhang et al. [397], Gopinath et al. [398], Herrera-Rivera et al. [399], Joshi et al. [400], Sun et al. [364], and Adeyemi and Fawole [401]. Smart packaging with antifungal capabilities could control the growth of toxigenic fungi, prevent the accumulation of mycotoxins, prolong the shelf life of food, and improve food safety.
The growing concern for food safety has prompted research into innovative strategies to mitigate food contamination by toxigenic fungi and mycotoxins. In recent decades, MNPs such as silver (Ag), copper (Cu), copper oxide (CuO), zinc oxide (ZnO), and iron oxide (Fe2O3, Fe3O4) have proven significant potential in the prevention and control of toxigenic fungi and the reduction of mycotoxins in various matrices. In this context, this review indicates that these MNPs have emerged as a promising tool due to their exceptional antifungal properties. These properties are derived from their high surface-to-volume ratio, which allows for greater interaction with fungal cells, and their ability to generate ROS that affect fungal cell integrity and disrupt essential metabolic processes.
In the near future, significant advances in the design of engineered NPs capable of selectively targeting specific toxigenic species and strains of Aspergillus, Fusarium, Penicillium, Alternaria, and Claviceps are expected to improve the efficiency and specificity of these NPs. The surface functionalization of NPs with specific ligands has the potential to enhance their interaction with key fungal structures while minimizing adverse effects on humans, animals, plants, and beneficial microorganisms.
Another promising area that is already experiencing growth is the incorporation of MNPs into active food packaging systems. These materials offer antifungal protection and can also act as sensors that detect the presence of fungi or mycotoxins, alerting to contamination in real time. This application is especially relevant to products such as cereals, nuts, coffee, spices, and dairy products, which are prone to spoilage.
It is imperative to prioritize the mitigation of NP toxicity and the enhancement of food safety. Notwithstanding their advantages, the utilization of MNPs gives rise to concerns regarding their toxicity to humans, animals, and the environment in general. Consequently, the design and development of biodegradable or biocompatible coated NPs that maintain their antifungal efficacy without generating significant risks to human health is crucial for future research endeavors. Toxicological evaluation at the cellular and systemic levels, as well as bioaccumulation and metabolization studies, will be essential.
Of particular relevance will be the development of hybrid technologies and synergies. The development of hybrid technologies, combining NPs with other natural antifungal compounds (e.g., essential oils or phenolic extracts), could enhance synergistic effects, allowing the use of lower concentrations and thus reducing the associated risks. Additionally, green nanotechnology, which utilizes biogenic synthesis of NPs with plant or microbial extracts, offers a sustainable alternative that could facilitate regulatory and societal acceptance.
Additionally, it will be imperative to deliberate on the implementation of NPs in agricultural and post-harvest systems. Beyond the realm of food processing, MNPs have the potential to play a crucial role in fungal and mycotoxin control during agricultural production and post-harvest storage. The development of effective formulations and their application on surfaces and coatings for grain, antifungal sprays, or seed treatments could prevent fungal contamination from the outset, reducing economic losses and enhancing food safety and security on a global scale.