The deficiency of nutrients in food crops is a major issue affecting the health of human beings, mainly in underdeveloped areas. Despite the development in the methods of food fortification, several barriers such as lack of proper regulations and smaller public-private partnerships hinder its successful implementation in society. Consequently, genetic and agronomic biofortification has been suggested as the potential techniques for fortifying the nutrients in diets. However, the time-consuming nature and restricted available diversity in the targeted crop gene pool limit the benefits of genetic biofortification. In agronomic biofortification, organic fertilizers face the problem of prolonged duration of nutrients release and lesser content of minerals; while in inorganic fertilizers, the large-sized fertilizers (greater than 100 nm) suffer from volatilization and leaching losses. The application of nanotechnology in agriculture holds enormous potential to cope with these challenges. The utility of nanomaterials for wheat biofortification gains its importance by supplying the appropriate dose of fertilizer at the appropriate time diminishing the environmental concerns and smoothening the process of nutrient uptake and absorption. Wheat is a major crop whose nano-biofortification can largely handle the issue of malnutrition and nutrients deficiency in human beings. Though several research experiments have been conducted at small levels to see the effects of nano-biofortification on wheat plants, a review article providing an overview of such studies and summarizing the benefits and outcomes of wheat nano-biofortification is still lacking. Although a number of review articles are available on the role of nanotechnology in wheat crop, these are mostly focused on the role of nanoparticles in alleviating biotic and abiotic stress conditions in wheat. None of them focused on the prospects of nanotechnology for wheat biofortification.
1. Introduction
Food and Agriculture Organization of the United Nations revealed a prevalence of 9.9 percent undernourishment projecting that more than 700 million people faced hunger in the world in 2020 [
1]. Additionally, more than 2 billion people are influenced by another form of malnutrition caused by the insufficient intake of micronutrients and vitamins and frequently known as hidden hunger [
2,
3]. A main reason behind this prevalence of malnutrition is the focus of our agricultural strategies toward increasing the crop production quantity and not quality. This led to a dearth of crucial nutrients in grain crops and consequently, among their consumers. Although the consumers have modified their food patterns and added nutritional food items such as dairy products, vegetables, fruits, and legumes to their diets, still a major population suffers from nutritional deficiencies [
4]. This emphasizes the need of a nutritional revolution to enhance the nutritional value of crops [
4,
5]. Thus, agriculturists have diverted their focus toward employing several techniques to develop nutrient-rich crops.
Biofortification or “biological fortification” is one of such techniques that allow the growing of crops rich in nutrients at comparatively lower cost with increased accessibility to the human population. It also increases variability in the present nutrient content in the crops. Basically, two main types of biofortification, genetic and agronomic biofortification are being applied to increase the nutritional quality of crop products [
6,
7]. Both these methods offer an inexpensive strategy of supplying nutritious food to poor or undernourished people [
8] and provide a sustainable, enduring and economical approach to deal with the issue of malnutrition. However, both these methods have their own limitations.
Genetic biofortification involves both transgenic and conventional breeding approaches (Figure 1). Transgenic approach allows the transfer and expression of nutrient-based genes across different species fortifying even the crops with least nutritional value [
9], and also reduces the anti-nutrients activity that regulates the bioavailability of nutrients in plants [
2]. However, despite its positive aspects, transgenic approach needs a large amount of effort in terms of expense and time during the research [
10]. Moreover, the reduced acceptance of transgenic crops among the farmers and community and difficult regulatory strategies for their commercialization also limit its benefits for the human population.
Similarly, biofortification via conventional breeding is the most acquired form of genetic biofortification due to its sustainable nature and great acceptability. The genotypes with higher nutrient value are crossed with the ones with comparatively less nutrient-rich but high-yielding genotypes [
4] (Figure 1). A large number of projects and programs such as HarvestPlus and Health grain Project have largely invested in the biofortification of different crops including whole grain cereals such as maize and wheat, sweet potato (
Ipomoea batatas), beans, pearl millet (
Pennisetum glaucum) through conventional breeding. However, despite the potential advantages of conventional breeding programs, sometimes it is extremely difficult to employ them in biofortification programs due to limited genetic variation in nutrient content in the gene pool, linkage drag, and the extremely long time required for the introgression of a trait in commercial cultivars [
11].
These limitations of genetic biofortification approaches suggest the implementation of agronomic strategies in biofortification programs. Agronomic biofortification mainly relies on the application of nutrient-containing fertilizers either through soil or foliar spray [
7]. The application of macronutrients like nitrogen (N), phosphorus (P), and potassium (K) and micronutrients such as copper (Cu), zinc (Zn), iron (Fe), manganese (Mn) via agronomic biofortification provided higher yields and protected a major human population from starvation [
12].
However, although agronomic biofortification is the most straightforward method among all the biofortification strategies, its success is dependent on several factors such as the type of nutrient to be supplied, differences in its uptake, movement, and accumulation across the plant tissues, and the property of the soil where the crop is grown [
2]. Thus, there is a dire need of alternative and advanced strategies to fortify grown crops.
Nanotechnology is one of such emerging technologies that can be progressively applied in agriculture to fortify the crops and that can largely deal with the drawbacks of genetic and traditional agronomic biofortification [
13]. Nanomaterials especially in the form of nanofertilizers (NFs) have the capacity to mitigate different stress conditions and enhance crop yield by increasing the nitrogen metabolism, seedling growth, carbohydrate and protein synthesis, photosynthesis, and increased translocation of nutrients from roots to leaves [
14]. Moreover, comparatively, a smaller amount of nanofertilizer application can effectively enhance the nutrient content with lesser harm to the surrounding environment due to its target-bound slow delivery [
15].
Wheat being the major staple crop has always been the center of attraction for different types of biofortification [
4]. Similar to other biofortification strategies, a number of studies revealing the positive outcomes of nanomaterials on wheat nutritional content have been conducted in greenhouses or small-scale field experiments to date [
16,
17,
18]. However, nanotechnology could not be effectively employed for wheat biofortification in large-scale agricultural programs.
To increase the employment of NFs in large scale wheat biofortification programs, it is necessary to have an overview of the effect of different nanomaterials and their application strategies on the nutrient content of the wheat genotypes [
19]. However, a review summarizing the utilization of nanomaterials for wheat biofortification is lacking till date. Hence, to fulfill this lack, in this review, the advancement in the employment of nanomaterials to fortify wheat seeds/crops with different nutrients until date has been deliberated. Moreover, the opportunities and benefits lying in the utilization of different nanotechnology-based methods for wheat biofortification have been discussed. Besides the challenges, nanobiofortified wheat crops hold a bright future to address the malnutrition challenge. The studies that have been discussed in this article can be taken into account while planning the application of different NFs in the wheat fields for the nutrient biofortification.
2. Advantages of Nanobiofortification over Agronomic Biofortification
Cereal grains including wheat, maize, and rice are the major food crops supplying around 60% of the daily calorie requirements in developing countries [
20]. Though these are rich in nutrient sources such as carbohydrates, fibers, proteins, lipids, vitamins, minerals, and phytochemicals as whole grain products, most of their nutritional components especially micronutrients are lost due to conventional processing [
21]. Consequently, fortification of wheat, rice, and maize flour with different vitamins and minerals especially iron and zinc is being emphasized in several countries that further enter in the food chain via flour-based food products [
22]. However, due to lack of sustainability in supplement fortification methods, other innovative strategies are required to ensure sustainable micronutrient levels in grain crops.
Agronomic biofortification has been considered as one of the efficient techniques increasing the mineral content in cereal crops at large scale. However, agronomic biofortification is not efficient to meet the expectations either due to poor quality of soil or due to less-efficient drainage system, and consequently, most of the applied fertilizers are wasted [
23]. A loss of around 40–70%, 80–90%, and 50–90% of applied N, P, and K fertilizers respectively have been reported previously [
14]. The requirement of their regular application in every season enhances the production costs to the farmers. Their repeated applications decrease the soil fertility and enhance salt content in soil leading to future losses in crop yields. The uncontrolled nutrient release via chemical fertilizers worsens the quality of the crop grains. Other than these issues, as the chemical fertilizers are being applied in greater amounts, the larger accumulation of toxic by-components including nitrate, heavy metals etc., in soil and water is one of the biggest challenges that agronomic biofortification poses on the environment. Accordingly, the disturbance in soil nutrient equilibrium, damage to soil fertility, and soil structure are the long-term consequences of the application of chemical fertilizers [
24] (
Figure 1). Consequently, there is a crucial need to find an efficient strategy to enhance quantity and quality of crops without increasing the annual consumption of chemical fertilizers.
Figure 1. Different strategies used for wheat biofortification. The left side of the figure explains the wheat biofortification strategies other than nanobiofortification and their drawbacks. The right side of the figure provides a summary of nanobiofortification including its target, entry points of nanofertilizers in plants, and the advantages of nanomaterials (Fe—iron, Zn—zinc, Cu—Copper, NPK—nitrogen, phosphorus and potassium) [
14,
24,
25].
Nanotechnology could provide possible solutions to several drawbacks of agronomic biofortification. Several properties of nanomaterials such as high sorption capacity, slow and controlled release at target sites, and high surface to volume ratio make them appropriate for nanofertilizers production [
25]. The encapsulation of nutrients with nanomaterials leads to efficient absorption of nutrients by plants due to slow or control release of nanoparticles, and easy penetration of biological barriers by nanoparticles entering the plant vascular system [
14,
26,
27]. This steady long-term delivery of plants via nanofertilizers allows enhanced crop growth as compared to conventional fertilizers [
25]. As nanofertilizers are added in small amounts, these also prevent soil to get burdened with the by-products of chemical fertilizers [
28] and reduces the environmental hazards. Contrary to chemical fertilizers, nanofertilizers can be synthesized and supplied according to the nutritional demand of the crop and status of the soil nutrients using biosensors [
29]. Additionally, as compared to chemical fertilizers, nanofertilizers enable high bioavailability of minerals to the plants due to their smaller size, high reactivity, and higher surface area [
30]. Thus, due to these mentioned advantages of nanofertilizers over the chemical fertilizers, these have been constantly being preferred for wheat biofortification nowadays.
3. Wheat Micronutrients Nanobiofortification via Seed Priming
Seed priming is a method that enhances the plant’s potential for nutrients uptake and translocation [
52]. This method provides hydration to seeds in a regulated manner up to the germination stage but before the protrusion of radical. In seed priming, seeds are treated with different amendments prior to sowing so that those can proceed toward different biochemical and metabolic progressions required for germination [
61]. This stimulates different physiological processes in plants to deal with devastating effects of abiotic stresses and enhancing the nutritive value of crops along with their yield [
52,
62,
63]. Seed priming not only decreases the duration of seedling emergence but also allows uniform germination with enhanced germination rate [
64,
65,
66,
67]. The fortification of nutrient crops by seed priming via conventional chemicals and fertilizers has been in practice since last several decades. Seed priming with NPs can further improve seed metabolism, deliver nutrients more efficiently than conventional forms, and have the benefits that nanofertilizers possess over the conventional fertilizers [
68]. Several studies have utilized NPs for the priming of wheat seeds to fortify the staple crop with nutrients (
Table 1,
Figure 2). Elhaj Baddar and Unrine [
47] suggested that ZnO NPs can be effectively used to treat wheat seeds to enhance Zn nutrition. They investigated the effect of seed treatment with bare ZnO NPs, dextran (DEX)- and dextran sulfate (DEX (SO
4))-coated ZnO NPs on wheat growth and Zn accumulation as compared to the conventional zinc sulphate (ZnSO
4) fertilizer. All the NPs-based formulations used in their study showed increased Zn concentration in wheat seeds in comparison with ZnSO
4, where bare ZnO and DEX-coated ZnO NPs showed maximum Zn concentration in shoot. The type of NP to be used for biofortification depends on the targeted objective as the surface chemistry influences the distribution of Zn within the plant and the growth of the tissue and biomass. The type of charges of the coating materials also affects the uptake, translocation, and accumulation of Zn in different wheat tissues [
69]. Moreover, the growth responses may vary according to both the concentration and the type of Zn treatment [
16]. The increase in the Zn concentration of shoots, roots, and grains of wheat plants can be proportionate [
16] or disproportionate [
17] to the increasing concentration of the applied ZnO NPs in priming of wheat seeds, though an increment is always observed. However, most of such studies have been conducted in hydroponics or pots and their efficacy in field experiments should be thoroughly determined. Seed priming with Zn and Fe NPs are not only seen to have a positive effect on the accumulation of these elements in wheat grains but is also known to have simultaneous suppressing effects on the toxicity of heavy metals such as cadmium (Cd), reducing their root, shoot, and grain accumulation [
17]. The wheat grain Cd content can be decreased below the threshold level of 0.2 mg kg
−1 when seeds are primed with higher Zn and Fe NPs. This decreased Cd concentration can be attributed to the simultaneous competition for uptake of Cd, Zn, and Fe at the root surface of wheat plants and consequently, improved uptake of Fe and Zn from the Fe
3O
4 and ZnO NPs [
17]. Thus, seed priming with NPs can be considered as a promising method of wheat Zn and Fe nanobiofortification not only in the normal growth conditions but also in the Cd stressed growth conditions and can also solve the problem of reduced germination rate of wheat seeds up to a certain extent.
Figure 2. An overview of the different methods used for Wheat Nanobiofortification, types of applied nanomaterials, and their outcome in the form of fortified nutrients. (Abbreviations in the figure: NPs- nanoparticles; ZnO—zinc oxide; dex—dextran; Fe2O3—ferric oxide; Fe3O4—ferrosoferric oxide; NPK—nitrogen, phosphorus, potassium; CNP—chitosan nanoparticles; B—boron, Fe—iron, Zn—zinc; Si—silicon; P—phosphorus; Cu—copper).
Table 1. Summary of the studies conducted using different forms nanomaterials for wheat nano-biofortification and the obtained impact in terms of nutrient content in seed grain in comparison to the control (no nanomaterial applied) and conventional agronomic biofortification applications (wherever present). (NC = No comparison was done with conventional fertilizers in this study).
Reference |
Type of Application |
Place of Trial |
Growth Medium |
On Application of Nanomaterial |
On Application of Conventional Fertilizers |
Applied Nanomaterial |
Amount Applied |
Nutrient Content in Grain without Application of Nanomaterial |
Nutrient Content in Grain on Addition of Nanomaterial |
Applied Conventional Fertilizer |
Amount Applied |
Nutrient Content in Grain on Addition of Conventional Fertilizers |
Deshpande et al. 2017 |
Foliar |
PVC columns |
Sand |
Zn-CNP |
≈20 mg g−1, ≈25mL |
≈15–19 µg g−1 DW Zn |
≈21–25 µg g−1 DW Zn |
NC |
Xue et al. 2017 |
Soil |
Pot |
Soil |
Nanochitin |
0.006 g kg−1 |
184.3 g kg−1 protein 58.6 mg kg−1 Fe 42.13 mg kg−1 Zn |
204.1 g kg−1 protein 65.39 mg kg−1 Fe 51.45 mg kg−1 Zn |
NC |
Zhang et al. 2017 |
Foliar |
Field |
Soil |
ZnO NP |
2 g L−1 at a rate of 1.2 kg ha−1 |
18.4 mg kg−1 (Year 1) Zn 23.6 mg kg−1 (Year 2) Zn |
26.5 mg kg−1 (Year 1) Zn 34.6 mg kg−1 (Year 2) Zn |
ZnSO4 |
7 g L−1 at a rate of 4.2 kg ha−1 |
21.1 mg/kg (Year 1) Zn 29.5 mg kg−1 (Year 2) Zn |
Dapkekar et al. 2018 |
Foliar |
Field |
Soil |
Zn-CNP |
40 mg L−1 |
39.5 µg g−1 |
53.3 µg g−1 |
ZnSO4 |
400 mg L−1 |
59.40 µg g−1 Zn |
Munir et al. 2018 |
Seed Priming |
Pot |
Soil |
ZnO NPs |
100 mg L−1 |
≈12 mg kg−1 DW Zn |
≈20 mg kg−1 DW Zn |
NC |
Burhan and Al-Hassan et al. 2019 |
Foliar |
Field |
Soil |
Nano NPK |
750:90:600 mg L−1 |
- |
13.5 % protein |
traditional NPK |
400 kg ha−1 urea, 200 kg ha−1 tri super phosphate, 100 kg ha−1 K2SO4 |
10.68 % protein |
Hussain et al. 2019 |
Foliar |
Pot |
Soil |
Fe3O4 NP |
20 mg kg−1 |
≈40 mg kg−1 DW Fe |
≈120 mg kg−1 DW Fe |
NC |
Hussain et al. 2019 |
Soil |
Pot |
Soil |
Fe3O4 NP |
20 mg kg−1 |
≈40 mg kg−1 DW Fe |
≈90 mg kg−1 DW Fe |
NC |
Khan et al. 2019 |
Soil |
Field |
Soil |
ZnO NP |
100 mg kg−1 |
≈20 mg kg−1 DW Zn |
≈45 mg kg−1 DW Zn |
NC |
Rizwan et al. 2019 |
Seed Priming |
Pot |
Soil |
ZnO NPs |
100 mg L−1 |
≈15 mg kg−1 DW Zn |
≈30 mg kg−1 DW Zn |
NC |
Rizwan et al. 2019 |
Seed Priming |
Pot |
Soil |
Fe NPs |
20 mg L−1 |
≈15 mg kg−1 DW Fe |
≈30 mg kg−1 DW Fe |
NC |
Sundaria et al. 2019 |
Seed Priming |
Pot Greenhouse |
Soil |
Fe2O3 NP |
600 ppm |
≈30–40 mg kg−1 DW Fe |
≈40–45 mg kg−1 DW Fe |
NC |
Adrees et al. 2020 |
Soil |
Pot |
Soil |
Fe2O3 NP |
100 mg kg−1 |
≈20 mg kg−1 DW Fe |
≈45 mg kg−1 DW Fe |
NC |
Adrees et al. 2021 |
Foliar |
Pot |
Soil |
ZnO NP |
100 mg L−1 |
≈22 mg kg−1 DW Zn |
≈45 mg kg−1 DW Zn |
NC |
Astaneh et al. 2021 |
Soil |
Field |
Soil |
Nano-chelated nitrogen |
240 kg ha−1 |
- |
69% protein 80 mg P 38 mg K |
Urea |
240 kg ha−1 |
17% protein 54 mg P 27 mg K |
Hussain et al. 2021 |
Foliar |
Field |
Soil |
Fe3O4 NP |
5 mg L−1 |
≈30 mg kg−1 DW Fe |
≈45 mg kg−1 DW Fe |
NC |
Hussain et al. 2021 |
Foliar |
Field |
Soil |
ZnO NP |
25 mg L−1 |
≈18 mg kg−1 DW Zn |
≈25 mg kg−1 DW Zn |
NC |
Sheoran et al. 2021 |
Foliar |
Pot |
Soil |
ZnO NP |
120 ppm |
17.48 mg g−1 FW Protein |
22.71 mg g−1 FW Protein |
Chemical Zn |
- |
19.91 mg g−1 FW Protein |
Seed priming of wheat seeds with different concentrations of FeO nanoparticles (IONPs) leads to the accumulation of different concentrations of Fe in wheat grains [
52]. A 12 h soaking of wheat seeds of two contrasting genotypes, IITR26 and WL711, showed a noticeable increase in grain Fe content even at the 25 ppm supply of IONPs. The former genotype with significantly higher concentrations of Fe, Zn, and manganese showed around 46% increase, while the later low-iron genotype showed an increment of 27% in grain Fe content. Wheat seeds priming with Fe showed stimulation of Fe transport mechanism and consequently, an accumulation of Fe in different sections of the seeds including the aleurone layer, endosperm, nucellar projection, and pigment strand of the crease [
52]. Thus, similar to Zn, for Fe biofortification also, wheat seed priming is an effective strategy for grain Fe acquisition and accumulation.
4. Wheat Micronutrients Nanobiofortification via Soil Fertilization
A number of studies revealed the increase in grain nutrient content on soil application of nanofertilizers as well (
Figure 2,
Table 1). The soil application of FeO nano fertilizers not only fortifies wheat grains with enhanced Fe content but also reduces the Cd accumulation under the combined Cd and drought-stressed wheat. The alleviation of oxidative stress developed by drought and Cd stress can be one of the major modes of action of IONPs. However, the success of this application also lays in the concentration of the NPS applied [
59]. Similar to Fe, Khan, et al. [
57] demonstrated the effect of soil application of ZnO NF on the growth of wheat plants in either only Cd-stressed soil or combined with water stress. While an increment in Cd content in wheat tissues was observed under drought stress, the Zn NF supply reduces the Cd uptake and accumulation by roots. An enhanced grain Zn concentration on ZnO NF application under Cd and drought-stressed environment emphasizes the utility of NF in wheat biofortification even in the contaminated soils. Moreover, it is observed that due to the slow release of nutrients, soil-applied ZnO NFs can stay in the soil and can be used by upcoming season’s crops.
Other than chemically synthesized NPs, biologically synthesized NPs which are popularly called “green NP” are gaining great attention nowadays due to their less toxic and environmental friendly nature along with their cost-effectiveness. Green FeO-NPs developed from bacterial strain
Pantoea ananatis RNT4 when applied to wheat plants via soil application co-ameliorates the effect of salinity and cadmium stress. At the same time, it can also biofortify the wheat plants with macronutrients, N, P, and K showing an increase of 33, 35, and 33% respectively on 100 mg kg
−1 supply of FeO-NPs as compared to no NPs treatment [
70]. Similarly, biogenic copper NPs synthesized from a copper-resistant strain of bacteria
Shigella flexneri SNT22 regulate the Cd stress by minimizing the movement of Cd from soil to plants and simultaneously increase the concentration of macronutrients such N, P, K, and Ca [
71]. This reduction in Cd translocation can be attributed to the struggle between Cd and CuNPs for entry into the root epidermal cells. Moreover, similar to ZnO and Fe NPs [
17], the restricted intake of Cd into wheat plants can be due to the use of the same transport channels by both Cu and Cd. Thus, the higher intake and consequently higher concentration of Cu in the plant restrict the Cd uptake [
72].
Other than increasing the biomass and grain yield, ZnO NPs are found to be non-toxic to plants even at a higher dose of 200 ppm. A significant increase in grain Zn content but not in leaf Zn of wheat plants was observed in the application of ZnO NPs via soil when compared with the ZnSO
4 fertilizers [
73]. Dimkpa, et al. [
74] determined the shared effect of soil application of ZnO nanoscale and bulk particles, organic fertilizer, and drought on the mineral accumulation of wheat grains. The bulk-ZnO and nano ZnO increase grain Zn content by 23 and 39% respectively as compared to control, while the addition of organic fertilizer can increase this content up to 94% under drought condition. This suggests that the addition of organic fertilizers along with the nano ZnO can be successfully applied in wheat biofortification programs especially in water-deficient growth environments. However, the reducing effect of both nano ZnO and bulk ZnO on wheat grain Fe content either in the presence or absence of organic fertilizer under drought conditions should be considered while programing a wheat biofortification program [
74].
The soil application of nanochitin, which is obtained from the hydrolysis of shrimp chitin, has a positive effect on the growth rate and yield of wheat plants. An increase of 22.1, 10.3, and 5% in Zn, Fe, and protein content of multi spike wheat; and an increment of 27, 32, and 33.4% in Zn, Fe, and protein content of large spike wheat was respectively obtained by treating wheat plants with 6 mg kg
−1 nanochitin [
75].
Although a number of studies have been conducted to observe the effect of soil application of nanomaterials on the nutrient content of different wheat tissues, none of the studies (except Astaneh et al. [
76]) have included conventional fertilizers in their experiments for comparison. The actual advantage of nanomaterials as compared to the conventional fertilizers for wheat biofortification can be properly understood by including both of them in the study designs.
5. Wheat Micronutrients Nanobiofortification via Foliar Fertilization
Foliar application of NFs has also been successfully employed for improving the quality of wheat grains under stressed and non-stressed conditions (
Figure 2). The foliar application of nano-Fe
2O
3 fertilizers on wheat plants is found to be more effective than the same amount of iron chelate and iron sulfate in increasing the chlorophyll, grain protein, and grainFe content [
77]. Similarly, the foliar application of Fe NPs was found to be more efficient than soil application in terms of Fe biofortification of wheat grains and reducing the grain Cd concentration under Cd-contaminated soil [
53]. However, both methods are promising for Fe nanobiofortification in wheat grains. Additionally, foliar application of NFs gives the advantage of their supply with pesticide application in the field. In contrast to soil application, foliar application of NF ensures the decreased passage of NPs to soil compartments and water, thereby reducing the chances of environmental pollution.
Some of the studies aimed to observe the effect of foliar application of nano ZnO fertilizer on the growth of wheat plants revealed more than 20% increment in grain protein content and a significant increase in photosynthetic pigments as compared to the conventional Zn fertilizer foliar spray [
78]. Along with increasing the wheat grain protein content, foliar application of nano ZnO also reduces the leaching of Zn into the soil after harvest [
78]. Moreover, a lesser amount of NPs is required for grain Zn biofortification in the foliar application as compared to the soil application [
18,
57]. Similar to the seed priming method [
52], the foliar application of ZnO NPs on wheat plants also lead to the accumulation of Zn in the crease and aleurone layer of the wheat grain along with a slight increment in endosperm Zn making it an appropriate method for Zn biofortification [
79]. The Zn accumulated in leaves from foliar supply of ZnO NFs can be efficiently utilized in metabolic processes of plants [
80,
81]. This accumulation can be attributed to the direct absorption of ZnO NPs by the leaf cuticles of wheat plants and their movement across the leaf epidermis via stomata, their release in apoplast and then adhesion to the mesophyll cells irrespective of the particle coating [
54,
82].
Similar to soil application of Fe NPs [
59], foliar application of ZnO NF also increases the plant growth, diminishes grain Cd, and enhances wheat grain Zn concentrations under Cd-stressed condition and under combined drought and Cd-stressed condition [
18]. The decrement in Cd concentrations on ZnO NFs application can be due to the higher Zn concentrations in plants. The Zn transport can be suppressed by the presence of higher Zn in plants as Cd and Zn may use the same transporters. The foliar-applied ZnO NPs improve the chlorophyll content of the treated plants, enhances the Zn transport, lowers the Cd content, increases the biomass, and also enhances the translocation of Zn to grains [
58]. Foliar application of both Fe and Zn NPs simultaneously on wheat plants grown in field conditions reduce the Cd uptake while enhances the Fe and Zn biofortification in wheat grains in Cd contaminated soils [
56]. This serves as a method for simultaneous Fe and Zn nanobiofortification of wheat. This simultaneous Fe-Zn biofortification of wheat grains in Cd contaminated soil is also possible when Si NPs are supplied with Fe and ZnO NPs [
56].
Chitosan (CHT) NPs which come under the category of nanomaterial-enhanced fertilizers or polymeric nanomaterials are actively being used for the delivery of agrochemicals in wheat [
50]. CHT that is the deacetylated form of chitin is the second most significant biopolymer after cellulose on earth. The efficiency of foliar application of zinc complexed chitosan nanoparticles (Zn-CNP) as nano-micronutrient carrier for wheat biofortification has been observed by Deshpande, et al. [
55]. Foliar ZnCNP not only enriches the durum wheat grains with 27 to 42% Zn in zinc-deficient growth conditions but also enhances its translocation to both leaf and seeds and inhibits the nutrient loss to the soil [
55]. Moreover, ZnCNPs are known to improve the Zn utilization efficiency of wheat plants if applied at right time in the right doses at the right place and then can Zn fortify the wheat grains by 36% even in the low Zn supply of 40 mg/L [
83]. This can be due to the effect of applied ZnCNP on the expression of the genes related to metal homeostasis, including the Fe and Zn-regulated transporter-like proteins that show a significant relationship with the grain Zn content [
84].
Si is the second most abundant element in the earth’s crust, which in the form of fertilizer decreases the pH and enhances the nutrient absorption from the soil. The soil and foliar application of SiO
2 NPs on wheat plants grown under drought stress conditions can increase wheat yield by 17.81% and 23.35% respectively [
85] with a simultaneous increase in grain protein content. Ahmadian, et al. [
86] observed the effect of foliar application of three different nano-chelated fertilizers comprising B, Zn, and Silicon (Si) on the growth rate and grain protein content of wheat plants grown under water-deficit conditions. The two-year experiment showed an increase in grain protein content by all the nano-fertilizers as compared to control either under fully irrigated or drought-stressed conditions. However, the increment was highest in nano-Zn treatment followed by nano-Si and it was higher in water-deficient condition than the fully irrigated regime. This increase might be due to the decrement in yield under drought conditions that leads to an increase in nitrogen content in grain [
85]. Moreover, as Zn supply is known to be affecting the gene expression and protein synthesis in plants, this might be a reason for the increased protein content [
87]. Similarly, Si fertilizer reduces the membrane damage in plants and thus, can be involved in increasing the protein content [
88].
The studies on wheat nanobiortification employing foliar application include both pot-based and field-based experiments (Table 1). However, most of them were Fe and Zn-based nanobiofortification. More studies should be conducted to fortify other micronutrients in wheat via nanobiofortification.
This entry is adapted from the peer-reviewed paper 10.3390/biology10111123