Skip to main content
Scientific Reports logoLink to Scientific Reports
. 2022 Nov 3;12:18552. doi: 10.1038/s41598-022-21834-9

The impact of nanofertilizer on agro-morphological criteria, yield, and genomic stability of common bean (Phaseolus vulgaris L.)

Dina M Salama 1,, M E Abd El-Aziz 2,, Essam A Shaaban 3, Samira A Osman 4, Mohamed S Abd El-Wahed 5
PMCID: PMC9633613  PMID: 36329080

Abstract

The use of agricultural fertilizers is one of the methods to beat the desired enormous increase in universal food production. The application of nanotechnology in agriculture is regarded as one of the promising approaches to elevate crop production. Whereas mineral nutrients play a crucial role in the growth and yield of the common bean. The experiments were conducted to investigate the application effect of micronutrients as nanoparticles (MN-NPs) on the common ben plants. The trial was performed in the field in El-Menofya, Egypt, through two seasons (2019 & 2020) in a randomized complete block design with three replicates and four combinations of MN-NPs (ZnO, MnO2 and MoO3) with concentrations 0, 10, 20, 30, 40 mg/L as a foliar application. The data exhibited that the foliar application of MN-NPs significantly upgraded the vegetative growth characters, flower number/plant, photosynthetic pigments, and yield. The concentration of 40 mg/L of MN-NPs leads to improving the vegetative growth, flowering number, and yield characteristics of the common bean. While the biochemical components varied in their response to MN-NPs combinations. The recommended MN-NPs concentration to ameliorate the common bean growth and yield was 40 mg/L.

Subject terms: Biochemistry, Genetics, Plant sciences, Nanoscience and technology

Introduction

It is anticipated in 2050 that the population of the world will rise to 9.6 billion1, which makes improving the yield of crops and grains will be required. Which pushed FAO2 to state that the yield of grain must be raised by 70 percent in 2050 to overcome these requests. Whereas the water sources and arable lands are restricted, agricultural fertilizers are the available approach to increase universal food production. So, it had been tended to raise the amount of added fertilizer to progress the yield of crops, but the increase in using traditional fertilizers for a prolonged period has produced large international environmental issues3,4. For that, researchers are girding to evolve fertilizers and their efficiency to increase agriculture production, as well as reducing environmental pollution. These nutrients are supplied as fertilizers, which are used to promote the growth and yield of plants. They are split into two main categories; macronutrients include nitrogen, phosphorus, and potassium (NPK), and micronutrients include calcium (Ca), mangnesium (Mn), zinc (Zn), iron (Fe), copper (Cu), molybdenum (Mo). These nutrients are regularly applied either by addition to the soil or as a foliar application5,6.

Zn is an essential micronutrient for plants, which used in small amounts for improve the activities of several enzymes and protein13. its deficiency causes the plants to suffer physiological stress due to its effect on several enzyme systems and metabolic actions Zn7. It plays an important role in the metabolism of proteins and carbohydrates, controlling the growth hormone8, and the production of tryptophan and growth hormone auxin9. Mahajan, Dhoke, and Khanna10 found that the growth of Vigna radiate and Cicer arietinum was improved by using 20 mg/L and 1 mg/L of ZnO-NPs, respectively. Prasad et al.11 demonstrated that the germination, growth and pod yield of peanuts was improved by using ZnO-NPs as a foliar than chelated ZnSO4.

Whereas manganese plays an essential role in the metabolism of nitrogen as well as photosynthesis where it acts as an electron store and travels them to the chlorophyll centers12. Also, it acts as is antioxidant e.g. dismutase to prevent spoilage of plant tissue by free radicals13. It is usually used in the range of 1–2 kg/ha14. Pradhan et al. showed that 0.05 mg/L of manganese nanoparticles increased the percentage of root and shoot length by 52% and 38% for mung bean plants in comparison to control15.

Molybdenum is an essential element for plant growth and biological fixation of nitrogen (BNF) by combining it with enzymes. Mo is important for nitrogen metabolism where it is accountable for the production of ammonium (NH3) from nitrogen. Its deficiency causes a lowering in the activity of molybdoenzymes and so decreasing plant growth and yield16. Taran et al.17 found that soaking chickpea seeds for 1–2 h in Mo-NPs solution ameliorates the growth and yield of chickpea plants.

Nanotechnology is a new trend that is being used in various industrial applications like pharmaceutical, packaging materials, sensors, conductors and agriculture18,19. It is participated in many stages of food preparation, from the beginning of cultivation to the packaging of the product for the consumer. Currently, it is used in the agricultural process to achieve the concept of smart agriculture or sustainable agriculture20. Where it can be used in the preparation of fertilizers, pesticides, and water purification that are used in agriculture processes as well as in remote sensing21. One way to improve crop production and conquer global food requirements is the implementation of nanotechnology in agricultural manure preparation2224. Indeed, nanotechnology has the potency to improve the entire current agrarian and food industry, by improving treatment methods for plant disease, and nutrient use efficiency26. Nowadays, nanofertilizers have great attention to be utilized instead of traditional fertilizers, which reached plant tissues via the root or leaves27. Where they were more effective in the planting process and lowing environmental impact by decreasing the losses to the surrounding environment28,29. Indeed, the NPs shape, size, or dosage affects the plants. Furthermore, the use of nanofertilizer could promote the existing functions or add new ones30,31.

DNA imprint is a remarkable molecular marker assay to illustrate the mutagenicity that occurs outstanding in the interplay between chemicals and plants32. Different molecular markers for example RAPD, SRAP, and ISSR can be performed to illustrate the variations that occur in DNA33. ISSRs have many advantages to being widely used such as; being easier and faster to use, inexpensive, as well no requirement for information about genomic sequences34,35. ISSRs have many advantages to being widely used such as; being easier and faster to use, inexpensive, as well no requirement for data about genomic sequences34. They are represented by the recognition of the changes that occur in the DNA profiles that may be formed as a new apparition or missing of some bands, or alteration in the intensities of other bands36.

The common beans (Phaseolus vulgaris L.) are one of the imperative food legumes for humans, which have huge differences in seed characteristics such as shape, volume, and color, besides growth habits, and ripeness. Their seeds are considered an important source of carbohydrates, vitamins, protein, and minerals, especially for developing countries humans besides they are the economic part. Therefore, it is counted in Egypt as one of the best essential vegetable crops planted for the local and export mart37,38.

Therefore, this study was conducted to investigate the influence of the combination of micronutrients (Zn, Mn and Mo) in nano-form as a foliar application on the quantity and quality of the common bean plus the genomic DNA stability.

Materials and methods

Materials

Common bean seeds (cv. Nebraska) purchased from the Agricultural Research Centre, Egypt. Agriculture traditional fertilizers such as sulfur, calcium superphosphate, potassium sulphate, and ammonium sulfate, bought from Abu Qir Company, Egypt. Manganese nitrate and citric acid were obtained from Sigma-Aldrich Company. Sodium hydroxide, ammonium hydroxide, zinc acetate, and ammonium molybdate were purchased from s.d. Fine-Chem.

Preparation of nanofertilizer

Zinc oxide nanoparticles (ZnO-NPs) were prepared by refluxing 3.942 g zinc acetate in 1L ethanol containing 1.44 g NaOH at 70 °C for 2 h. The fine white powder was obtained and purified by adding deionized water and then centrifugation for 10 min at 5000 rpm, after that the fine white powder which burned for 2 h at 500 °C to obtain ZnO-NPs39.

Manganese oxide nanoparticles (MnO2-NPs) were prepared thermally by dissolving Mn(NO3)2·4H2O in water (100 g/50 ml) at 100 °C under vigorous stirring for 10 min, after that the previous solution was heated in an oven to 100 °C for 24 h till black viscous liquid was achieved. The deionized water was added to the previous liquid and centrifugation for 15 min at 7000 rpm. The black particles were washed with deionized water and dried at 100 °C40.

Molybdenum oxide nanoparticles (MoO3-NPs) were prepared via a sol–gel method, where 11.6 g ammonium molybdate and 3.8 g citric acid were dissolved in distilled water under stirring. The pH was adjusted at 7 by ammonium hydroxide, and then heated to 250 °C for 1 h to get a powder, then burned for 120 min at 500 °C to get MoO3-NPs41.

Characterization

A transmission electron microscope (TEM; JEM-1230, Japan) was employed to illustrate the morphology and particle size of the nanoparticles, which operated at 120 kV, magnification of 6 × 105, and a resolution is 0.2 nm. While the geometry and purity of prepared nanoparticles were determined using a Philips X-ray diffractometer (PW 1930 generator, PW 1820 goniometer, and radiation source CuK).

Experiment layout

Experimental research and field studies on common bean plants obey the guidelines of the Ethics Committee in the National Research Centre.

The ground had been scrubbed, ploughed, and leveled in February, after that, it was divided into plots. The organic manure (cattle manure), calcium superphosphate (15.5% P2O5), agricultural sulfur, potassium sulphate (48% K2O), and ammonium sulphate (20.6% N) were added in the range 47.6 m3/ha, 476, 236, 120, and 118 kg/ha, respectively, during the soil preparation. After seeds germination, ammonium sulphate (236 kg/ha) was added. Before the second irrigation, ammonium sulphate and potassium sulphate were applied in quantities 238 and 120 kg/ha, respectively.

The common bean seeds (120 kg/ha) were cultivated on 3 March throughout two seasons 2019 and 2020 in clay ground in El-Monifia governorate, Egypt. Table S1 showed the physical and chemical characteristics of the soil. The samples of soil were collected from various sites of each plot from the depth of 0 to 20 cm, which were analyzed according to Cottenie et al.42. Two seeds per hole were sowed on one side of the ridge and 30 cm between holes while the distance between the ridges was 60 cm. The harvest was done after three months. The average weekly temperature ranged from 20 to 31 °C during the period of the cultivation (3 Mar–3Jun) as illustrated in Fig. S2.

The transactions

The common bean plants were sprayed after 20 days of sowing by a combined three nanofertilizer with various concentrations (0, 10, 20, 30, and 40 mg/L) as shown in Table 1. The treatments were performed in the morning (8 am) with one liter of suspended nanomaterials in water (pH 7.2) using a hand-pump garden sprayer. The experiment was set up in a complete randomized block design with three replicates.

Table 1.

The treatment recipe.

Treatment ZnO-NPs (mg/L) MnO2-NPs (mg/L) MoO3-NPs (mg/L)
T1 (control) 0 0 0
T2 10 10 10
T3 20 20 20
T4 30 30 30
T5 40 40 40

Agro-morphological criteria

Three random plants in vegetative growth stage were taken from each dealing (after 45 days of sowing) to determine various vegetative growth factors, for example, the length of plant and root, the numeral of leaves and flowers per plant, besides the weight of fresh and dry for plants. After 90 days of sowing (Harvest stage) three samples were taken to measure the weight and number of seeds and pods per plant, plus shelling percentage, seed index (weight of 100 seeds), the weight of seeds (t/ha) and shoot residues (kg/ha).

Chemical studies

Photosynthetic pigments

The fresh leaves were collected after 45 days of sowing to extract photosynthetic pigments using 85% acetone. The concentrations of chlorophyll a (Chl. a), chlorophyll b (Chl. b), and carotenoid (Cart.) were measured by UV/VIS spectrophotometer (TG 80, Germany) at 663, 644, and 452 nm, respectively, against a blank (85% acetone)43.

The concentration of the pigments was measured as µg/ml and calculated using the equations proposed by Jiang et al.44.

Chl a=10.3 E663-0.918E644μg/ml
Chl b=19.7E644-3.870E663μg/ml
Caro=4.2 E452-0.0264 Chl a+0.426 Chl bμg/ml.

Then concentrations of chlorophyll and carotenoids were expressed as mg/g fresh weight of plant material.

Proximate analysis

Fresh samples of leaves and seeds were dried at 60 °C in the oven till constant weight and then ground for proximate analysis by the standard methods according to AOAC45. The moisture content was calculated by weighing the sample before and after drying till a constant weight at 105 °C. The ash was obtained by burning at 550 °C for 6 h in a muffle furnace. The crude protein was measured by the Kjeldahl method (N × 6.25). The fiber content was calculated after digestion in acid (1.25%) then in alkali (1.25%) then extracting by ether. The total energy was calculated by the Atwater factor method [(9 × fat) + (4 × carbohydrate) + (4 × protein)] as described by Nwabueze46.

Minerals determination

Plant samples were ground and digested with H2SO4-H2O2. In the digested solutions, the concentration of potassium and phosphorus were determined by a spectrophotometer, while atomic absorption was used to measure the content of Zn, Mn, Fe and Cu47.

Statistical analysis

The statistical analysis of the obtained data was done according to the procedures described by Snedecor et al.48 to determine significant differences using LSD at a 5% level.

DNA purification and SCoT-PCR analysis

The plant genomic DNA was extracted and purified from leaves of the common bean using Gene Jet Plant Genomic DNA purification Mini Kits (Thermo scientific K0791). NanoDrop 1000 spectrophotometer (Thermo Scientific) was used to measure the quantitation of pure genomic DNA. Eight SCoT Primers with GC content between 50 and 72% (Table 2) were used in PCR reaction49. PCR amplification was achieved using Thermocycler (Bio-Rad). The PCR was programmed as follows: an initial denaturation one cycle for 3 min at 94 °C, followed by 35 cycles for 1 min at 94 °C, then for 1 min at 50 °C, and 2 min at 72 °C; the final extension at 72 °C for 5 min (one cycle) then held at 4 °C. Agarose gel was placed in 1X TAE buffer (1.2%) for running the amplified products at 100 V for 2 h. The Gel Documentation (Bio-Rad) was used for photographing the gel and then analyzed by the Total Lab program to find out the molecular size of each band.

Table 2.

Sequences of SCoT primers.

Ser. No Primer Sequence (5–3) GC%
1 SCoT-2 CAACAATGGCTACCACCC 56
2 SCoT-4 CAACAATGGCTACCACCT 50
3 SCoT-5 CAACAATGGCTACCACGA 50
4 SCoT-22 AACCATGGCTACCACCAC 56
5 SCoT-26 ACCATGGCTACCACCGTC 61
6 SCoT-34 ACCATGGCTACCACCGCA 61
7 SCoT-36 GCAACAATGGCTACCACC 56
8 SCoT-30 CCATGGCTACCACCGGCG 72

The Genomic Template Stability (GTS, %) was calculated as the following:

GTS=100-100an

where, (a) is the average number of the differences in DNA profiles, and (n) is the number of bands that were selected through control profiles of DNA.

Proteins banding pattern

Sodium Dodecyl Sulfate Polyacrylamide Gel Electrophoresis technique (SDS-PAGE) was performed according to Tsugama et al.50 to separate the proteins based on their molecular weight. The water-soluble proteins (W.S.P.) were extracted from the leaves of common bean plants in the seedling and flowering growth stage. BLUltra Prestained Protein Ladder (GeneDirex, Cat No. PM001-0500) was used as a protein marker. The extracted proteins were electrophoresed by vertical electrophoresis (Cleaver, UK), on 12% protein separating gel.

Toxicity test

In an oven at 105 °C, the common bean seeds were well dehydrated and then milled to a fine powder. An extract was obtained from this powder using water at two concentrations 0.1% and 1.0%. The toxicity of the samples was performed by using Microtox analyzer 500 (USA)51.

Results

Characteristics of nanofertilizer

Figure 1a illustrated the morphology of the prepared nanoparticles, which demonstrated that they had particle sizes less than 100 nm. TEM image of ZnO-NPs showed spherical particles with an average particle size of less than 50 nm, while MnO2-NPs had a uniform diamond shape with an average particle size of 70 nm. Instead, the MoO3-NPs showed the smallest size with a mean particle size of 10 nm.

Figure 1.

Figure 1

TEM image (a) and XRD pattern (b) of ZnO, MnO2, and MoO3-NPs.

Figure 1b showed the crystal structure of the ZnO, MnO2, and MoO3–NPs via using X-ray diffraction. The main peaks of ZnO-NPs obtained at 2θ = 32, 34.4, 36.4, 47.7°, and 56.7° are related to plans (100), (002), (101), (102) and (110), respectively39. Moreover, the peaks at 2θ (28.7 and 37.3°), (24.8 and 65°) and (42.82, 46.02, 56.65, and 59.3°) are corresponding to α-MnO2, γ-MnO2, and β-MnO2, respectively52. While the pattern of MoO3–NPs illustrates the peaks at 2θ = 17.9, 19.9, 26.1, 34.5, 39.3, and 49° resemble the orthorhombic crystal structure of MoO353. The XRD patterns emphasize the pureness of the prepared oxide nanoparticles.

Vegetative growth characters

The foliar implementation of MN-NPs as a fertilizer has significantly affected the vegetative outgrowth traits of the common bean as expressed as plant and root length, number of leaves and flowers per plant, and fresh and dry weight for plant throughout both seasons 2019 & 2020 in comparison with the control (Table 3). The improvement of vegetative characters (length of plant and root, number of leaves per plant, plant weight for plants (fresh and dry weight)), and the numeral of flowers/plants were associated with raising the concentricity of MN-NPs. The concentration of 40 mg/L gave the greatest values of the vegetative characters where the plant length was (57.3–59.0 cm), root length was (28.0–27.0 cm), the number of leaves was (35.3–34.3) fresh weight was (156.4–159.6 g), dry weight was (29.8–30.3 g), and the numeral of flowers/plants was (84.0–85.0) during both seasons 2019 & 2020, respectively. The obtained consequences recorded a significant effect in the vegetative characters at LSD 5% which are as follows: plant length (1.58 and 1.89), root length (2.09 and 1.42), number of leaves per plant (2.41 and 2.12), number of flowers per plant (2.78 and 2.84), fresh weight for plants (7.87 and 8.34), and dry weight for plants (1.53 and 1.59), during agriculture seasons 2019 and 2020.

Table 3.

Effect of MN-NPS on vegetative growth characters of common bean plants during two successive seasons 2019 and 2020.

Treatment Plant length (cm) Root length (cm) No. leaves/plant No. flowers/plant Fresh plant weight
(g)
Dry plant weight (g)
2019 2020 2019 2020 2019 2020 2019 2020 2019 2020 2019 2020
T1 53.3 53.7 16.3 16.8 29.3 29.7 59.3 63.3 130.9 131.3 22.9 24.6
T2 47.7 48.3 17.8 17.2 29.7 30.3 62.7 64.3 133.3 131.4 24.6 24.1
T3 53.7 54.7 22.3 21.3 29.3 30.3 64.3 66.7 143.0 145.0 26.2 26.1
T4 55.5 56.3 24.3 23.3 30.3 31.3 68.7 70.3 150.2 153.0 26.9 27.6
T5 57.3 59.0 28.0 27.0 35.3 34.3 84.0 85.0 156.4 159.3 29.8 30.3
LSD at 5% 1.58 1.89 2.09 1.42 2.41 2.12 2.78 2.84 7.87 8.34 1.53 1.59

Common bean yield

The data in Table 4 displayed that the implementation of MN-NPs (ZnO, MnO2, and MoO3) significantly increased the yield and its components of the common bean plant through seasons 2019 and 2020, in comparison to control. Increasing the concentration led to enhancement of the yield and its components except for shelling percentage, this was related to 10 mg/L concentration. The highest MN-NPs concentration (40 mg/L) gave the greatest values of the yield and its components characters, where the number of pods/plant (37.3–38.7), weight of pods/plant (58.5–60.7 g), number of seeds /plant (10.6–105.0), seed yield (2.24–2.34 t/ha) and shoot residue (913.0–931.3 kg/ha) during the two seasons 2019 & 2020, respectively. From these we found that the increasing percentage of the numeral of pods/plant is (89.3–93.5%), the weight of pods/plant is (26.6–29.2), the numeral of seeds per plant is (58.7–51.5), the shelling percentage is (23.2–25.5), seed yield is (55.6–61.4) and shoot residue is (51.4–49.4) through the seasons 2019 & 2020, respectively.

Table 4.

Effect of MN-NPs on yield and its components of common bean plant during two seasons.

Treatment No. seeds/ plant No. pods/ plant Weight (g)/ plant Shelling percentage Seed index
(100 seeds
weight (g))
Seeds yield
(t/ha)
Shoot residues
(kg/ha)
Poods Seeds Shoot residues
2019 2020 2019 2020 2019 2020 2019 2020 2019 2020 2019 2020 2019 2020 2019 2020 2019 2020
T1 67.0 69.3 19.7 20.0 46.2 47.0 26.3 26.4 11.0 11.3 56.7 56.0 39.1 37.9 1.44 1.45 603.2 623.3
T2 90.0 94.0 28.0 28.7 53.9 54.5 39.5 38.5 13.1 12.8 73.4 70.7 43.9 41.1 2.17 2.12 720.5 702.2
T3 100.3 101.0 33.0 34.0 55.9 56.8 33.3 33.0 14.4 14.6 59.6 58.6 33.1 32.6 1.83 1.82 792.0 801.2
T4 103.0 102.3 33.7 34.3 56.4 59.0 38.5 42.3 14.5 15.1 68.1 71.7 37.3 41.6 2.12 2.32 799.3 832.3
T5 106.3 105.0 37.3 38.7 58.5 60.7 40.8 42.6 16.6 16.9 69.9 70.3 38.5 40.8 2.24 2.34 913.0 931.3
LSD at 5% 3.64 4.75 1.02 0.80 2.67 3.94 1.73 1.12 0.67 0.53 3.54 3.39 2.27 2.88 0.10 0.06 36.66 29.24

Chemical studies

Photosynthetic pigments

It appeared from Fig. 2 that the implementation of MN-NPs remarkably increased the content chl. a, chl. b, total chl., and carotenoid (photosynthetic pigments) in the common bean plant in compression to control through seasons 2019 and 2020. Increasing photosynthetic pigments content was related to enhancing MN-NPs concentration. Application of 40 mg/L (T5) gave the maximum values of chl. a, chl. b, and total chl. content, while the uppermost content of carotenoids was found with 20 mg/L of MN-NPs (T3).

Figure 2.

Figure 2

Effect of MN-NPs on the average value of the two seasons for the Chl a, Chl b, total chlorophyll, and carotenoids.

Proximate components

The micronutrient NPs appeared a significant increment in proximate components of common bean leaves such as carbohydrate, protein, lipid, fiber, ash, and total energy in comparison with the control during two seasons (Table 5). The MN-NPs at a concentration of 40 mg/L resulted in a significant increase in the carbohydrate percentage (43.4 and 42.9%) as well as the total energy (285.1 and 284.6 kcal/g) in the common bean leaves compared to other concentrations during two seasons (Table 5). On the contrary, the protein percentage (20.7 and 20.5%) gave the best value at a concentration 20 mg/L of MN-NPs followed by plants treated with a concentration 30 mg/L of MN-NPs. The lipid (4.91 and 5.0%) and ash (18.7 and 19.1%) content in leaves of common bean increased with a concentration 30 mg/L of MN-NPs as compared to other concentrations. The highest percentage of moisture (7.33 and 7.37%) and fiber (11.93 and 11.97%) was recorded with plants grown without MN-NPs.

Table 5.

Effect of micronutrients nanoparticles on proximate components of common bean.

Treatment Moisture
(%)
Carbohydrate
(%)
Protein
(%)
Lipid
(%)
Fiber
(%)
Ash
(%)
Total energy
(Kcal/g)
2019 2020 2019 2020 2019 2020 2019 2020 2019 2020 2019 2020 2019 2020
Leaves
T1 7.33 7.37 39.5 39.6 18.2 18.3 4.73 4.80 11.93 11.97 18.4 18.0 273.1 274.8
T2 6.56 6.52 39.1 39.0 19.5 19.3 4.65 4.68 11.45 11.30 18.7 19.1 276.5 275.7
T3 7.07 7.10 38.0 37.5 20.7 20.5 4.82 4.87 11.57 11.38 17.8 18.7 278.2 275.7
T4 7.17 7.12 37.7 37.4 20.3 20.2 4.91 5.00 11.15 11.10 18.7 19.1 276.4 275.6
T5 6.64 6.59 43.4 42.9 18.4 18.6 4.20 4.29 11.06 11.06 16.3 16.6 285.1 284.6
LSD at 5% 0.23 0.25 0.19 0.37 0.24 0.36 0.35 0.36 0.72 0.69 0.98 51.03 3.57 3.41
Seeds
T1 6.4 6.3 39.2 39.4 20.2 20.0 4.00 3.90 13.1 13.2 17.1 17.2 273.6 272.7
T2 9.6 9.5 43.6 43.0 19.2 19.3 5.65 5.60 12.5 12.3 9.4 10.3 302.3 299.3
T3 10.4 10.5 44.5 43.5 17.9 18.0 5.64 5.63 12.3 12.1 9.3 10.4 300.2 296.3
T4 10.6 10.6 45.4 44.9 17.7 17.8 5.69 5.73 11.6 11.6 9.0 9.4 303.5 302.1
T5 11.9 11.6 40.3 40.7 18.0 17.9 5.66 5.68 12.5 12.2 11.6 11.9 284.0 285.5
LSD at 5% 0.18 0.29 1.56 2.00 0.89 0.79 0.06 0.11 1.93 2.02 3.11 2.82 7.22 7.58

In addition, Table 5 shows that the MN-NPs significantly affect LSD at 5% in proximate components of common bean seeds during the 2019 and 2020 seasons. Micronutrient as NPs with concentration 30 mg/L (T4) were more effective on the content of carbohydrate (45.4 and 44.9%), lipid (5.69 and 5.73%) and total energy (303.5 and 302.1 kcal/g), while 40 mg/L (T5) gave the best values of moisture percentages (11.9 and 11.6%), during two successive seasons 2019 and 2020. On the other hand, the increasing seeds content of protein (20.2 and 20.0%), fiber (13.1 and 13.2%), and ash (17.1 and 17.2%) were related to (T1) control during two cultivated seasons 2019 and 2020.

Minerals content

Data in Table 6 displayed that the minerals content in the leaves and seeds of common bean plants were significantly enhanced with micronutrient NPs application compared with control during (2019 & 2020) seasons. The content of phosphorus (0.30 and 0.31%) and potassium (3.43 and 3.43%) in leaves of common bean plants appeared the highest value with control as compared to MN-NPs. Contrariwise, the content of leaves of zinc (31 and 30 mg/L),and manganese (63 and 62 mg/L) enhanced with the lowest concentration of MN-NPs (10 mg/L) followed by plants treated with MN-NPs at a concentration of 20 mg/L, during two seasons 2019 and 2020. The concentration of MN-NPs (20 mg/L) improved the content of iron in leaves (760.0 and 756.6 mg/L) and in descending order the plants processed with MN-NPs at a concentration of 10 mg/L, during two agriculture seasons 2019 & 2020. The nitrogen percentage (3.31 and 3.31%) was boosted with the application of MN-NPs at a concentration of 30 mg/L as compared with other treatments.

Table 6.

Effect of nanofertilizer on minerals of common bean leaves and seeds during two seasons.

Treatment N % P % K % Zn (mg/L) Mn (mg/L) Fe (mg/L) Cu (mg/L)
2019 2020 2019 2020 2019 2020 2019 2020 2019 2020 2019 2020 2019 2020
Leaves
T1 2.90 2.87 0.30 0.31 3.43 3.43 20.00 19.33 44.0 43.5 611.3 609.9 8.73 8.57
T2 2.83 2.79 0.21 0.20 2.90 2.65 31.00 30.00 63.0 62.0 727.3 724.6 13.07 12.97
T3 3.11 3.07 0.29 0.31 2.64 2.87 20.90 20.67 59.7 58.8 760.2 756.6 13.00 12.67
T4 3.31 3.31 0.26 0.29 3.05 3.24 19.70 19.40 56.3 55.6 725.3 721.3 13.00 12.63
T5 3.22 3.18 0.29 0.31 3.02 2.66 18.40 18.20 48.5 49.2 600.1 597.8 11.30 11.47
LSD at 5% 0.02 0.04 0.04 0.05 0.14 0.13 0.53 0.54 1.29 1.48 8.19 9.02 0.38 0.57
Seeds
T1 2.93 2.87 0.32 0.31 2.51 2.45 20.2 20.0 4.1 4.2 44.4 43.7 9.1 9.3
T2 3.22 3.19 0.25 0.24 2.40 2.37 23.5 23.2 5.9 5.8 17.3 18.0 12.0 11.8
T3 3.05 3.02 0.26 0.26 2.44 2.38 23.1 23.2 6.2 6.0 21.8 22.4 10.7 10.8
T4 2.84 2.77 0.26 0.28 2.57 2.48 26.4 26.1 6.0 6.0 20.7 21.5 10.5 10.7
T5 2.81 2.71 0.32 0.31 2.15 2.21 21.5 21.7 4.3 4.5 20.4 20.5 9.1 9.3
LSD at 5% 0.09 0.13 0.01 0.02 0.12 0.13 0.52 0.45 0.10 0.09 0.70 0.67 0.24 0.28

The effect of different concentrations of MN-NPs on endogenous minerals (Nitrogen, phosphorus, potassium, zinc, manganese, iron, and copper) in seeds of the common bean plant was presented in Table 6. Data was obvious that the foliar application of MN-NPs had a significant effect on the minerals of common bean seeds. The best increment of nitrogen (3.22 and 3.19%), and copper (12 and 11.8 mg/L) were obtained in seeds of common bean plants sprayed with MN-NPs at a concentration of 10 mg/L followed by plants supplied with MN-NPs at a concentration of 20 mg/L, during two cultivated seasons 2019 and 2020. Conversely, the highest content of manganese in seeds was recorded with MN-NPs at a concentration of 20 mg/L followed by plants sprayed with MN-NPs at a concentration of 30 mg/L. The content of potassium (2.57 and 2.48%) and zinc (26.4 and 26.1 mg/L) was significantly increased as a result of using MN-NPs as a foliar fertilizer at a concentration of 30 mg/L as compared to other concentrations, during two successive seasons 2019 and 2020. The maximum content of phosphorus (0.32 and 0.31%) was achieved with the highest concentration of MN-NPs (40 mg/L) as compared to other concentrations, during two agriculture seasons 2019 and 2020.

Effect of different nanofertilizer on genomic DNA using SCoT-PCR Marker

Eight primers were utilized for the SCoT amplification to determine the variation in DNA fingerprints of Phaseolus Vulgare L. exposed to various concentrations of MN-NPs and the control (Figs. 3, and Table 7). The original figure obtained from SCoT-PCR was illustrated in S3. The eight SCoT primers distinguished 88 DNA fragments in controls with a number of bands 8, 9, 14, 16, 8, 13, 8, and 12 corresponding to SCoT-2, SCoT-4, SCoT-5, SCoT-22, SCoT-26, SCoT-34, SCoT-36 and SCoT-30, respectively.

Figure 3.

Figure 3

The effect of MN-NPs concentrations on the genomic DNA for common bean by SCoT-PCR. M: DNA ladder 100 bp, 1: T1, 2: T2, 3: T3, 4: T4, 5: T5.

Table 7.

The Influence of MN-NPs concentrations on genomic DNA of the common bean by SCoT -PCR. (+ : present, −: absent).

Ser. No SCoT primers Total number of bands Allele size range (bp) Mono-morphic bands Poly-morphic bands (+ ve) Unique bands (−ve) Unique bands Polymorphism
%
Molecular Size (bp) T1 T2 T3 T4 T5
1 SCoT-2 8 1610–260 7 1 0 0 12.5% 1610  +   + 
2 SCoT-4 9 1500–210 7 2 1 0 22.22% 1500  +   +   + 
210  + 
3 SCoT-5 14 2400–250 12 2 0 1 14.28% 870  +   + 
495  +   +   +   + 
4 SCoT-22 16 3800–240 12 4 0 4 25% 3800  +   +   +   + 
3530  +   +   +   + 
955  +   +   +   + 
870  +   +   +   + 
5 SCoT-26 8 980–220 6 2 0 2 25% 625  +   +   +   + 
220  +   +   +   + 
6 SCoT-34 13 2165–230 8 5 0 1 38.46% 2165  +   +   + 
1680  +   +   + 
1220  +   +   + 
990  +   +   +   + 
645  +   +   + 
7 SCoT-36 8 945–215 7 1 0 0 12.5% 285  +   +   + 
8 SCoT-30 12 2210–280 8 4 2 2 33.33% 2210  + 
1975  + 
1080  +   +   +   + 
885  +   +   +   + 
Total 88 67 21 3 10
Average 11 8.375 2.625 23.86%

The total number of bands from DNA amplification using SCoT-2, SCoT-26, and SCoT-36 primers were eight bands ranging from 1610 to 260, 980 to 220, and 945 to 215 bp, respectively. Where, SCoT-26 primer had two –ve unique bands at 625 and 220 bp, which disappeared in control (T1) while amplified in all studied concentrations of nanofertilizers.

The amplification of SCoT-4 primer gave nine bands with molecular sizes ranging from 1500 to 210 bp and the polymorphism was 22.22%. In addition, it gave one + ve unique band at molecular size 210 bp for T1. While the amplification of SCoT-5 primer gave a total number of bands (fourteen) which ranged from 2400 to 250 bp with a polymorphism of 14.28%. There is one –ve unique band at 495 bp in the transaction T5 only.

In primer SCoT-22, the total number of bands were sixteen ranging from 3800 to 240 bp with four polymorphic bands at molecular size 3800, 3530, 955, and 870 bp that were present in all transactions except the transaction T5. In addition, the primer SCoT-34 had a total number of bands thirteen ranging from 2165 to 230 bp with five polymorphic bands (38.46% polymorphism). The polymorphic bands had one –ve unique band at 990 bp that disappeared in T1 only.

Finally, the amplification of the SCoT-30 primer gave twelve bands ranging from 2210 to 280 bp with four polymorphic bands (33.33% polymorphism). There had two -ve unique bands at 1080 and 885 bp that disappeared only in T1, also there had two + ve unique at 2210 and 1975 bp in the transaction T5.

Effect of different MN-NPs concentrations on protein profiles using SDS-PAGE

The expression of some genes encoding proteins because of MN-NPs effects on common beans illustrates in Fig. 4 and Table 8. The original figure obtained from protein profiles using SDS-PAGE was illustrated in S4. Twenty-seven bands were obtained in the seedling stage with twenty-three monomorphic bands, while in the flowering stage; twenty-six bands were obtained with twenty-one monomorphic bands. There were four polymorphic bands in the seedling stage but five polymorphic bands were obtained in the flowering stage presented.

Figure 4.

Figure 4

Effect of different concentrations of MN-NPs on protein banding patterns of W.S.P. for common bean in both seedling and flowering stages. Where M is protein marker, 1:5 are T1:5 in seedling stages, while 6:10 are T1:5 in flowering stages

Table 8.

Effect of MN-NPs concentration on electrophoretic of W.S.P. banding patterns of common bean in seedling and flowering stages. (+ : present, −: absent).

graphic file with name 41598_2022_21834_Tab8_HTML.jpg

The data displayed that both stages were characterized by the presence of protein at Mw 50 Kilo Daltons (KDa) in the transaction T4 only also the protein at Mw 130 KDa present in the transaction T1 only. While the protein at Mw 120 KDa is absent in transactions T3 and T4 only. In the flowering stage, the protein at Mw 57 KDa is absent only in T4, and the protein at Mw 45 KDa is absent in transactions T3 and T4. While in the seedling stage, the protein at Mw 140 KDa is absent in control while present in the other transactions.

Toxicity test

The common bean seeds obtained from various treatments using the combination of ZnO + MnO2 + MoO3 -NPs showed that they are not nontoxic. Where the effective concentration (EC50) as obtained from using a Microtox analyzer for all samples was less than 100 indicates they are eco-friendly. This result is in the same direction as the study of Jiang et. al54 on the toxicity of silver nitrate (AgNO3) and silver nanoparticles (Ag-NPs), who found that Ag-NPs were less toxic than AgNO3.

Discussion

The supply requirement of essential nutrients for the plant at different growth stages is needful to raise the quality and yield of the crop. In this experiment, we applied the essential macronutrients (NPK) as soil fertilizer and different concentrations of micronutrients as a foliar nanofertilizer at vegetative growth stage, which significantly improved common bean growth and yield parameters. The application of micronutrients via foliar spray is important to increase the use efficiency of micronutrients and promote crop yields, Where the absorption of nutrients is faster and supplies the plant with the required amount of nutrients55,56. Volkweiss57 noted that the foliar application of nanoparticle fertilizing is a buoyant method for using micronutrients since it demands lower rates and micronutrients that are not directly affected by the soil, that being so averting the losses by stabilization. Li et al.58 showed that the affirmative impact of the external application of ZnO NPs improved shoot/root biomass of cucumber plant.

The combined MN-NPs affect the physiological processes of the plant. Where they were the reason for improving the vegetative growth characteristics as presented in Tables 3 and 4, which reflected on increasing pods and seeds synthesis per plant, as a result, stimulating plant enzymes and translocation of metabolites from vegetative organs to the seeds. Also, the application of MN-NPs was necessary to improve and stimulate the physiological processes of plants reflected in enhancing the synthesis of photosynthetic pigments content in common bean leaves. The improvement of the content of the photosynthetic pigment enhances the performance of the plants hereby the vegetative growth characteristics were promoted under MN-NPs treatments59. Kheirizadeh et al.60 reported that the negative effects of salinity on the growth character, yield and nutrients accumulation in barley plants could be reduced by foliar application of nano fertilizer. They found that Zn and Fe in nano-form improve the growth character and yield due to their critical role in biochemical and physiological activities.

Indeed, owing to the size of nanomaterials, they are gradually absorbed and are directly participated in biochemical reactions, improving the plant enzymes' action, reinforcing the exchange of nitrates to ammonia, production of amino acids and enzymes, growing plant transpiration, and photosynthesis operation, plus to improve nitrogen and carbon nutrition, subsequently, nanomaterials have direct effects on mineral nutrition of plants6163. Zn stress affects either by metabolic processes or by absorption competition on the plant's content of nutrients. Hossain et al. showed that excess zinc leads to a reduction of iron and magnesium accumulation while the copper content increases. This may be due to that Zn and Cu use the same transporters64. Whereas, Feigl et al.65 stated that treatment of Brassica by Zn significantly increased the content of Cu and Fe but decreased the content of Mn in the roots in comparison to the control.

Moreover, the MN-NPs played an important role in the movement of metabolites from the leaves to the seeds. Where it is the main reason for the improvement of the content of carbohydrates and lipids in the seeds of the common bean gotten from the treatment T4 as shown in Table 5. Indeed, Zn plays an important role in the metabolism of proteins and carbohydrates8, while manganese affects the metabolism of nitrogen12, whereas molybdenum is an essential element for the biological fixation of nitrogen (BNF)16. The results obtained can be attributed to the interaction of nanomaterials with plants which results in different morphological and physiological in plants, according to the characteristic of the nanomaterials. Distinctive characteristics such as size, form, chemical structure, and active dosage affect on the implementation of nanomaterials. The favorable and unfavorable influences of nanomaterials on plant expansion depend on the size, composition, concentration, and physical and chemical properties of nanomaterials as well as the plant20,30. These consequences were consistent with those got from SCoT-PCR analysis (Fig. 3 and Table 7). The difference in proximate components and minerals in leaves and seeds of common bean plant may be due to the genetic mutation on genomic DNA. Where new bands were appeared and other were disappeared in the SCoT-PCR analysis as effect of the various concentration of MN-NPs on the plant.

Start codon targeted (SCoT) marker is a new method based on the short-conserved region in plant genes surrounding the translation inception codon or beginning codon49. It is longer than other markers where it consists of 18-mer, which is connected to functional genes and their corresponding characters66. The alterations in the priming places lead to changes in the homologous recombination and annealing conditions that give rise to the evanescence of specific bands and the occurrence of novel bands67.

The data in Table 7 displayed that the more effective concentration of MN-NPs on the genomic DNA was 40 mg/l compared to the control. Some bands vanished and others were evidenced in all studied transactions compared to control, this might be described by the uppermost concentration of nanofertilizer acting as a genotoxic agent producing DNA damage in the priming locations. This agrees with Ghosh et al.68, who detected that high concentrations of ZnO-NPs lead to a rise in the chromosome aberrations of Allium cepa and break the DNA strand. Also, as the concentration of ZnO-NPs was growing the content of ROS was increased in Vicia faba and Nicotiana tabacum, this leads to ROS reaching genomic DNA and causing DNA strand damage.

The genotoxicity effect as a result of the change in the frequencies of bases pair mutation could be qualitatively determined by studying the genomic template stability percentage (GTS%), which relates to the degree of DNA variation69. Table 9 illustrates that the values of GTS% which are reduced with raising the concentration MN-NPs indicate that all MN-NPs concentrations had a significant effect on the plants' genomic DNA. Previous studies found that raising the implementation of Ag-NPs on the tomato up to 80 mg/l70, ZnO-NPs on the fava bean plant up to 50 mg/l71, and MoO3-NPs on common bean up to mg/l36 caused decreasing the GTS%.

Table 9.

Number of new appeared ( +) and disappeared (−) bands as related to control and GTS % in common bean plants under the effect of MN-NPs using eight SCoT primers.

Ser
No
Primer name Treatments
T2 T3 T4 T5 T1
1 SCoT-2  +  8
1 (1610 bp) 1 (1610 bp) 1 (1610 bp)
2 SCoT-4  +  9
1 (210 bp) 1 (210 bp) 2 (1500, 210 bp) 2 (1500, 210 bp)
3 SCoT-5  +  14
1 (870 bp) 1 (870 bp) 2 (870, 495 bp)
4 SCoT-22  +  16
4 (3800, 3530, 955, 870 bp)
5 SCoT-26  +  2 (625, 220 bp) 2 (625, 220 bp) 2 (625, 220 bp) 2 (625, 220 bp) 8
6 SCoT-34  +  1 (990 bp) 5 (2165, 1680, 1220, 990, 645) 5 (2165, 1680, 1220, 990, 645) 5 (2165, 1680, 1220, 990, 645) 13
7 SCoT-36  +  8
1 (285 bp) 1 (285 bp)
8 SCoT-30  +  2 (1080, 885 bp) 2 (1080, 885 bp) 2 (1080, 885 bp) 4 (2210, 1975, 1080, 885 bp) 12
Total number of bands 6 12 14 21 88
% of GTS 93.18% 86.36% 84.1% 76.14% 100%

The effect of MN-NPs on the expression of some genes encoding proteins of common bean may be owing to some metabolic processes in plants that had been affected by nanomaterials application72,73. This is because of the absorption, accumulation, and translocation of nanomaterials in plants, moreover these particles may be interacting with plant cells causing a modification of gene expression74.

Many researchers illustrated that nanoparticles are up to 40 times less toxic than salts and that are more efficient63,75. Moreover, Shaban et al. studied the effect of plants fertilized by nano-fertilizer on the rats’ health. They found that the common bean fertilized either by ZnO76 or by MoO3-NPs77 does not cause any harm to rats that feed on it.

Conclusions

This study illustrated that using the combination of MN-NPs (ZnO, MnO2, and MoO3) at the concentration 40 mg/L of each one improves the vegetative growth characters of common bean plants as well as enhances the seeds production to 2.24 and 2.34 t/ha during two seasons 2019 and 2020, respectively. We can recommend that the combination of MN-NPs with the concentration of 40 mg/L could be sprayed on common bean plants to ameliorate their growth, yield, genetic, and some quality characters. It can be deduced that micronutrient in the form of nanoparticles have a hopeful future as a nano-fertilizer in the cultivation strip for applications based on nano-biotechnology.

Supplementary Information

Acknowledgements

We express gratitude to the National Research Centre for reinforcing this research through project No 12050109.

Author contributions

D.S.: carried out the agriculture experiment, study the Agro- morphological criteria, share in the chemical analysis, analyzed the data, and shared in writing the manuscript. M.A.: preparation and characterization of nanomaterials, analysis of the data, and sharing in writing the manuscript. S.O.: do the SCoT-PCR Analysis and SDS-PAGE Protein Banding Patterns and share in writing the manuscript. M.A.: design the experimental and share in the Chemical analysis and the discussion of data. E.S.: design the experimental, discussion of data and sharing in writing the manuscript.

Funding

Open access funding provided by The Science, Technology & Innovation Funding Authority (STDF) in cooperation with The Egyptian Knowledge Bank (EKB).

Data availability

The datasets used and/or analyzed during the current study are available from the corresponding author upon reasonable request.

Competing interests

The authors declare no competing interests.

Footnotes

Publisher's note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Contributor Information

Dina M. Salama, Email: dinasalama@ymail.com

M. E. Abd El-Aziz, Email: Mahmoud_essam12@yahoo.com

Supplementary Information

The online version contains supplementary material available at 10.1038/s41598-022-21834-9.

References

  • 1.United Nations, N. Y. World population prospects The 2000 revision. Vol. 1: comprehensive tables. (2001).
  • 2.FAO. How to Feed the World in 2050. <http://www.fao.org/fileadmin/templates/wsfs/docs/expert_paper/How_to_Feed_the_World_in_2050.pdf>, 2009).
  • 3.Abd El-Aziz M, et al. Preparation and characterization of chitosan/polyacrylic acid/copper nanocomposites and their impact on onion production. Int. J. Biol. Macromol. 2019;123:856–865. doi: 10.1016/j.ijbiomac.2018.11.155. [DOI] [PubMed] [Google Scholar]
  • 4.Shaviv A, Mikkelsen R. Controlled-release fertilizers to increase efficiency of nutrient use and minimize environmental degradation-A review. Fertil. Res. 1993;35:1–12. doi: 10.1007/BF00750215. [DOI] [Google Scholar]
  • 5.Corradini E, De Moura M, Mattoso L. A preliminary study of the incorparation of NPK fertilizer into chitosan nanoparticles. Express Polymer Lett. 2010;4:509–515. doi: 10.3144/expresspolymlett.2010.64. [DOI] [Google Scholar]
  • 6.Salama DM, Abd El-Aziz ME, Osman SA, Abd Elwahed MSA, Shaaban EA. Foliar spraying of MnO2-NPs and its effect on vegetative growth, production, genomic stability, and chemical quality of the common dry bean. Arab J. Basic Appl. Sci. 2022;29:26–39. doi: 10.1080/25765299.2022.2032921. [DOI] [Google Scholar]
  • 7.Noulas C, Tziouvalekas M, Karyotis T. Zinc in soils, water and food crops. J. Trace Elem. Med Biol. 2018;49:252–260. doi: 10.1016/j.jtemb.2018.02.009. [DOI] [PubMed] [Google Scholar]
  • 8.Fageria, N. K., Baligar, V. C. & Clark, R. B. in Advances in Agronomy Vol. 77 (ed Donald L. Sparks) 185–268 (Academic Press, 2002).
  • 9.Alloway, B. Zinc in soil and crop nutrition. Zinc in plant nutrition. International Zinc Association, Bruselas (2004).
  • 10.Mahajan P, Dhoke S, Khanna A. Effect of nano-ZnO particle suspension on growth of mung (Vigna radiata) and gram (Cicer arietinum) seedlings using plant agar method. J. Nanotechnol. 2011 doi: 10.1155/2011/696535. [DOI] [Google Scholar]
  • 11.Prasad T, et al. Effect of nanoscale zinc oxide particles on the germination, growth and yield of peanut. J. Plant Nutr. 2012;35:905–927. doi: 10.1080/01904167.2012.663443. [DOI] [Google Scholar]
  • 12.Millaleo R, Reyes-Díaz M, Ivanov A, Mora M, Alberdi M. Manganese as essential and toxic element for plants: transport, accumulation and resistance mechanisms. J. Soil Sci. Plant Nutr. 2010;10:470–481. doi: 10.4067/S0718-95162010000200008. [DOI] [Google Scholar]
  • 13.Mousavi SR, Shahsavari M, Rezaei M. A general overview on manganese (Mn) importance for crops production. Aust. J. Basic Appl. Sci. 2011;5:1799–1803. [Google Scholar]
  • 14.Draycott AP, Christenson DR. Nutrients for sugar beet production: Soil-plant relationships. UK: Cabi; 2003. [Google Scholar]
  • 15.Pradhan S, et al. Photochemical modulation of biosafe manganese nanoparticles on Vigna radiata: a detailed molecular, biochemical, and biophysical study. Environ. Sci. Technol. 2013;47:13122–13131. doi: 10.1021/es402659t. [DOI] [PubMed] [Google Scholar]
  • 16.Campo RJ, Araujo RS, Hungria M. Molybdenum-enriched soybean seeds enhance N accumulation, seed yield, and seed protein content in Brazil. Field Crops Res. 2009;110:219–224. doi: 10.1016/j.fcr.2008.09.001. [DOI] [Google Scholar]
  • 17.Taran NY, et al. The effect of colloidal solution of molybdenum nanoparticles on the microbial composition in rhizosphere of Cicer arietinum L. Nanoscale Res. Lett. 2014;9:289–297. doi: 10.1186/1556-276X-9-289. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Shaban E, et al. Evaluation of acute oral toxicity of zinc oxide nanoparticles in rats. Egypt. J. Chem. 2021;64:4591–4600. doi: 10.21608/ejchem.2021.80810.4003. [DOI] [Google Scholar]
  • 19.Hassan MM, Taha RA, Abd El-Aziz ME, Shaaban EA, Ibrahim EA. Impact of nano-zinc-oxide as an alternative source of zinc in date palm culture media. Plant Cell Tissue Organ Cult. (PCTOC) 2022;150:73–84. doi: 10.1007/s11240-022-02235-2. [DOI] [Google Scholar]
  • 20.Salama DM, Abd El-Aziz ME, Rizk FA, Abd Elwahed MSA. Applications of nanotechnology on vegetable crops. Chemosphere. 2021;266:129026. doi: 10.1016/j.chemosphere.2020.129026. [DOI] [PubMed] [Google Scholar]
  • 21.Liu R, Lal R. Potentials of engineered nanoparticles as fertilizers for increasing agronomic productions. Sci. Total Environ. 2015;514:131–139. doi: 10.1016/j.scitotenv.2015.01.104. [DOI] [PubMed] [Google Scholar]
  • 22.Shebl A, Hassan A, Salama DM, Abd El-Aziz ME, Abd Elwahed MS. Template-free microwave-assisted hydrothermal synthesis of manganese zinc ferrite as a nanofertilizer for squash plant (Cucurbita pepo L.) Heliyon. 2020;6:e03596. doi: 10.1016/j.heliyon.2020.e03596. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 23.Mastronardi, E., Tsae, P., Zhang, X., Monreal, C. & DeRosa, M. C. in Nanotechnologies in food and agriculture 25–67 (Springer, 2015).
  • 24.Shebl A, Hassan A, Salama DM, Abd El-Aziz M, Abd Elwahed MS. Green synthesis of nanofertilizers and their application as a foliar for Cucurbita pepo L. J. Nanomater. 2019 doi: 10.1155/2019/3476347. [DOI] [Google Scholar]
  • 25.El-Mohamedy RS, Abd El-Aziz ME, Kamel S. Antifungal activity of chitosan nanoparticles against some plant pathogenic fungi in vitro. Agric. Eng. Int. CIGR J. 2019;21:201–209. [Google Scholar]
  • 26.Sozer N, Kokini JL. Nanotechnology and its applications in the food sector. Trends Biotechnol. 2009;27:82–89. doi: 10.1016/j.tibtech.2008.10.010. [DOI] [PubMed] [Google Scholar]
  • 27.Wang P, Lombi E, Zhao F-J, Kopittke PM. Nanotechnology: a new opportunity in plant sciences. Trends Plant Sci. 2016;21:699–712. doi: 10.1016/j.tplants.2016.04.005. [DOI] [PubMed] [Google Scholar]
  • 28.Ghormade V, Deshpande MV, Paknikar KM. Perspectives for nano-biotechnology enabled protection and nutrition of plants. Biotechnol. Adv. 2011;29:792–803. doi: 10.1016/j.biotechadv.2011.06.007. [DOI] [PubMed] [Google Scholar]
  • 29.AbdElwahed M, AbdEl-Aziz ME, Shaaban E, Salama DM. New trend to use biochar as foliar application for wheat plants (Triticum Aestivum) J. Plant Nutr. 2019;42:1180–1191. doi: 10.1080/01904167.2019.1609503. [DOI] [Google Scholar]
  • 30.Siddiqui, M. H., Al-Whaibi, M. H., Firoz, M. & Al-Khaishany, M. Y. in Nanotechnology and Plant Sciences 19–35 (Springer, 2015).
  • 31.Mahmoud SH, Salama DM, Abd El-Aziz ME. Effect of chitosan and chitosan nanoparticles on growth, productivity and chemical quality of green snap bean. Biosci. Res. 2018;15:4307–4321. [Google Scholar]
  • 32.Cenkci S, Yıldız M, Ciğerci İH, Konuk M, Bozdağ A. Toxic chemicals-induced genotoxicity detected by random amplified polymorphic DNA (RAPD) in bean (Phaseolus vulgaris L.) seedlings. Chemosphere. 2009;76:900–906. doi: 10.1016/j.chemosphere.2009.05.001. [DOI] [PubMed] [Google Scholar]
  • 33.Al-Qurainy F. Application of inter simple sequence repeat (ISSR marker) to detect genotoxic effect of heavy metals on Eruca sativa (L.) Afr. J. Biotechnol. 2010;9:467–474. doi: 10.5897/AJB09.729. [DOI] [Google Scholar]
  • 34.Semagn K, Bjørnstad Å, Ndjiondjop M. An overview of molecular marker methods for plants. Afr. J. Biotech. 2006;5:2540–2568. [Google Scholar]
  • 35.Salama DM, Osman SA, Abd El-Aziz M, Elwahed MSA, Shaaban E. Effect of zinc oxide nanoparticles on the growth, genomic DNA, production and the quality of common dry bean (Phaseolus vulgaris) Biocatal. Agric. Biotechnol. 2019;18:101083. doi: 10.1016/j.bcab.2019.101083. [DOI] [Google Scholar]
  • 36.Osman SA, Salama DM, AbdEl-Aziz ME, Shaaban EA, AbdElwahed MS. The influence of MoO3-NPs on agro-morphological criteria, genomic stability of DNA, biochemical assay, and production of common dry bean (Phaseolus vulgaris L.) Plant Physiol. Biochem. 2020;151:77–87. doi: 10.1016/j.plaphy.2020.03.009. [DOI] [PubMed] [Google Scholar]
  • 37.Abdel-Hakim W, Moustafa Y, Gheeth R. Foliar application of some chemical treatments and planting date affecting snap bean (Phaseolus vulgaris L.) plants grown in Egypt. J. Hortic. Sci. Ornam. Plants. 2012;4:307–317. [Google Scholar]
  • 38.Salama DM, Abd El-Aziz ME, El-Naggar ME, Shaaban EA, Abd El-Wahed MS. Synthesis of an eco-friendly nanocomposite fertilizer for common bean based on carbon nanoparticles from agricultural waste biochar. Pedosphere. 2021;31:923–933. doi: 10.1016/S1002-0160(21)60024-3. [DOI] [Google Scholar]
  • 39.Chen JH, Cheng C-Y, Chiu W-Y, Lee C-F, Liang N-Y. Synthesis of ZnO/polystyrene composites particles by Pickering emulsion polymerization. Eur. Polymer J. 2008;44:3271–3279. doi: 10.1016/j.eurpolymj.2008.07.023. [DOI] [Google Scholar]
  • 40.Najafpour MM, Rahimi F, Amini M, Nayeri S, Bagherzadeh M. A very simple method to synthesize nano-sized manganese oxide: an efficient catalyst for water oxidation and epoxidation of olefins. Dalton Trans. 2012;41:11026–11031. doi: 10.1039/c2dt30553d. [DOI] [PubMed] [Google Scholar]
  • 41.Fernandes CI, Capelli SC, Vaz PD, Nunes CD. Highly selective and recyclable MoO3 nanoparticles in epoxidation catalysis. Appl. Catal. A-Gen. 2015;504:344–350. doi: 10.1016/j.apcata.2015.02.027. [DOI] [Google Scholar]
  • 42.Cottenie, A., Verlo, M., Kjekens, L. & Camerlynch, R. Chemical analysis of plant and soil. Laboratory of Analytical Agrochemistry. 42, 80–284 (State University, Gent, Belgium, 1982).
  • 43.Metzner H, Rau H, Senger H. Untersuchungen zur synchronisierbarkeit einzelner pigmentmangel-mutanten von Chlorella. Planta. 1965;65:186–194. doi: 10.1007/BF00384998. [DOI] [Google Scholar]
  • 44.Jiang J, et al. Estimation of leaf traits from reflectance measurements: comparison between methods based on vegetation indices and several versions of the PROSPECT model. Plant Methods. 2018;14:23. doi: 10.1186/s13007-018-0291-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 45.Jayant M, et al. Protein requirement of juvenile striped catfish, Pangasianodon hypophthalmus. Aquac. Int. 2018;26:375–389. doi: 10.1007/s10499-017-0216-0. [DOI] [Google Scholar]
  • 46.Nwabueze T. Nitrogen solubility index and amino acid profile of extruded African breadfruit (T. africana) blends. Niger. Food J. 2007 doi: 10.4314/nifoj.v25i1.33651. [DOI] [Google Scholar]
  • 47.Nielsen SS. Food analysis. Boston: Springer; 2010. [Google Scholar]
  • 48.Snedecor GW, Cochran WG. Statistical methods, 8thEdn. Iowa State Univ. Press Iowa; 1989. [Google Scholar]
  • 49.Collard BCY, Mackill DJ. Start codon targeted (SCoT) polymorphism: A simple, novel DNA marker technique for generating gene-targeted markers in plants. Plant Mol. Biol. Report. 2009;27:86–93. doi: 10.1007/s11105-008-0060-5. [DOI] [Google Scholar]
  • 50.Tsugama D, Liu S, Takano T. A rapid chemical method for lysing Arabidopsis cells for protein analysis. Plant Methods. 2011;7:22. doi: 10.1186/1746-4811-7-22. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 51.Johnson BT. Small-Scale Freshwater Toxicity Investigations. Dordrecht: Springer; 2005. pp. 69–105. [Google Scholar]
  • 52.Devaraj S, Munichandraiah N. Effect of crystallographic structure of MnO2 on its electrochemical capacitance properties. J. Phys. Chem. C. 2008;112:4406–4417. doi: 10.1021/jp7108785. [DOI] [Google Scholar]
  • 53.Kim W-S, Kim H-C, Hong S-H. Gas sensing properties of MoO3 nanoparticles synthesized by solvothermal method. J. Nanoparticle Res. 2010;12:1889–1896. doi: 10.1007/s11051-009-9751-6. [DOI] [Google Scholar]
  • 54.Jiang H-S, Li M, Chang F-Y, Li W, Yin L-Y. Physiological analysis of silver nanoparticles and AgNO3 toxicity to Spirodela polyrhiza. Environ. Toxicol. Chem. 2012;31:1880–1886. doi: 10.1002/etc.1899. [DOI] [PubMed] [Google Scholar]
  • 55.Sapkota TB, et al. Crop nutrient management using Nutrient Expert improves yield, increases farmers’ income and reduces greenhouse gas emissions. Sci. Rep. 2021;11:1564. doi: 10.1038/s41598-020-79883-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 56.Bana RS, et al. Foliar nutrient supplementation with micronutrient-embedded fertilizer increases biofortification, soil biological activity and productivity of eggplant. Sci. Rep. 2022;12:5146. doi: 10.1038/s41598-022-09247-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 57.Volkweiss S. Fontes e métodos de aplicação [Sources and application methods] Micronutr. na Agric. [Micronutrients in Agriculture] 1991;1:391–412. [Google Scholar]
  • 58.Li S, et al. Comparative physiological and metabolomic analyses revealed that foliar spraying with zinc oxide and silica nanoparticles modulates metabolite profiles in cucumber (Cucumis sativus L.) Food Energy Secur. 2021;10:e269. doi: 10.1002/fes3.269. [DOI] [Google Scholar]
  • 59.Babaei K, Seyed Sharifi R, Pirzad A, Khalilzadeh R. Effects of bio fertilizer and nano Zn-Fe oxide on physiological traits, antioxidant enzymes activity and yield of wheat (Triticum aestivum L.) under salinity stress. J. Plant Interact. 2017;12:381–389. doi: 10.1080/17429145.2017.1371798. [DOI] [Google Scholar]
  • 60.Kheirizadeh Arough Y, Seyed Sharifi R, Sedghi M, Barmaki M. Effect of zinc and bio fertilizers on antioxidant enzymes activity, chlorophyll content, soluble sugars and proline in triticale under salinity condition. Not. Bot. Horti Agrobot. Cluj-Napoca. 2016;44:116–124. doi: 10.15835/nbha44110224. [DOI] [Google Scholar]
  • 61.Colvin VL. The potential environmental impact of engineered nanomaterials. Nat. Biotechnol. 2003;21:1166. doi: 10.1038/nbt875. [DOI] [PubMed] [Google Scholar]
  • 62.Kole C, et al. Nanobiotechnology can boost crop production and quality: first evidence from increased plant biomass, fruit yield and phytomedicine content in bitter melon (Momordica charantia) Bmc Biotechnol. 2013;13:37–47. doi: 10.1186/1472-6750-13-37. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 63.Poddar, K., Vijayan, J., Ray, S. & Adak, T. in Biotechnology for Sustainable Agriculture 281–303 (Elsevier, 2018).
  • 64.Hossain MB, Sawada A, Noda K, Kawasaki M. Hydathode function and changes in contents of elements in eddo exposed to zinc in hydroponic solution. Plant Prod. Sci. 2017;20:423–433. doi: 10.1080/1343943X.2017.1383167. [DOI] [Google Scholar]
  • 65.Feigl G, et al. Zinc induces distinct changes in the metabolism of reactive oxygen and nitrogen species (ROS and RNS) in the roots of two Brassica species with different sensitivity to zinc stress. Ann. Bot. 2015;116:613–625. doi: 10.1093/aob/mcu246. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 66.Mulpuri S, Muddanuru T, Francis G. Start codon targeted (SCoT) polymorphism in toxic and non-toxic accessions of Jatropha curcas L. and development of a codominant SCAR marker. Plant Sci. 2013;207:117–127. doi: 10.1016/j.plantsci.2013.02.013. [DOI] [PubMed] [Google Scholar]
  • 67.Atienzar FA, Jha AN. The random amplified polymorphic DNA (RAPD) assay and related techniques applied to genotoxicity and carcinogenesis studies: a critical review. Mutat. Res.-Rev. Mutat. 2006;613:76–102. doi: 10.1016/j.mrrev.2006.06.001. [DOI] [PubMed] [Google Scholar]
  • 68.Ghosh M, et al. Effects of ZnO nanoparticles in plants: Cytotoxicity, genotoxicity, deregulation of antioxidant defenses, and cell-cycle arrest. Mutat. Res. Genet. Toxicol. Environ. Mutagen. 2016;807:25–32. doi: 10.1016/j.mrgentox.2016.07.006. [DOI] [PubMed] [Google Scholar]
  • 69.Savva D. The use of arbitrarily primed PCR (AP-PCR) fingerprinting to detect exposure to genotoxic chemicals. Ecotoxicology. 2000;9:341–353. doi: 10.1023/A:1026577326366. [DOI] [Google Scholar]
  • 70.Çekiç FÖ, Ekinci S, İnal MS, Özakça D. Silver nanoparticles induced genotoxicity and oxidative stress in tomato plants. Turk. J. Biol. 2017;41:700–707. doi: 10.3906/biy-1608-36. [DOI] [Google Scholar]
  • 71.Mahmoud H. Molecular and cytogenetic assessment of zinc nanoparticles on Vicia faba plant cells. Egypt. J. Exp. Biol. (Bot.) 2019;15:39–49. doi: 10.5455/egyjebb.20181108065044. [DOI] [Google Scholar]
  • 72.Nair G, Chung IM. Impact of copper oxide nanoparticles exposure on Arabidopsis thaliana growth, root system development, root lignificaion, and molecular level changes. Environ. Sci. Pollut. Res. Int. 2014;21:12709–12722. doi: 10.1007/s11356-014-3210-3. [DOI] [PubMed] [Google Scholar]
  • 73.Hossain Z, Mustafa G, Komatsu S. Plant responses to nanoparticle stress. Int. J. Mol. Sci. 2015;16:26644–26653. doi: 10.3390/ijms161125980. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 74.Khiew, P. et al. in Palm Oil: Nutrition, Uses and Impacts 189–219 (Nova Science Publishers, Inc., 2011).
  • 75.Li X, et al. Effects of physicochemical properties of nanomaterials on their toxicity. J. Biomed. Mater. Res. Part A. 2015;103:2499–2507. doi: 10.1002/jbm.a.35384. [DOI] [PubMed] [Google Scholar]
  • 76.Shaban EE, et al. The effect of white kidney bean fertilized with nano-zinc on nutritional and biochemical aspects in rats. Biotechnol. Rep. 2019;23:e00357. doi: 10.1016/j.btre.2019.e00357. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 77.Shaban EE, et al. The effect of exposure to MoO3-NP and common bean fertilized by MoO3-NPs on biochemical, hematological, and histopathological parameters in rats. Sci. Rep. 2022;12:12074. doi: 10.1038/s41598-022-16022-8. [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Data Availability Statement

The datasets used and/or analyzed during the current study are available from the corresponding author upon reasonable request.


Articles from Scientific Reports are provided here courtesy of Nature Publishing Group

RESOURCES