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. 2024 Jan 4;19(1):8. doi: 10.1186/s11671-023-03953-y

Ionome mapping and amino acid metabolome profiling of Phaseolus vulgaris L. seeds imbibed with computationally informed phytoengineered copper sulphide nanoparticles

Nandipha L Botha 1,2,✉, Karen J Cloete 1,2,✉, Žiga Šmit 3,4, Kristina Isaković 4, Mahmood Akbari 1,2, Razieh Morad 1,2, Itani Madiba 1,2, Oladipupo Moyinoluwa David 5, Luis P M Santos 6, Admire Dube 5, Primoz Pelicon 4, Malik Maaza 1,2
PMCID: PMC10767113  PMID: 38175418

Abstract

This study reports the effects of a computationally informed and avocado-seed mediated Phyto engineered CuS nanoparticles as fertilizing agent on the ionome and amino acid metabolome of Pinto bean seeds using both bench top and ion beam analytical techniques. Physico-chemical analysis of the Phyto engineered nanoparticles with scanning-electron microscopy, transmission electron microscopy, X-ray diffraction, and Fourier Transform Infrared Spectroscopy confirmed the presence of CuS nanoparticles. Molecular dynamics simulations to investigate the interaction of some active phytocompounds in avocado seeds that act as reducing agents with the nano-digenite further showed that 4-hydroxybenzoic acid had a higher affinity for interacting with the nanoparticle’s surface than other active compounds. Seeds treated with the digenite nanoparticles exhibited a unique ionome distribution pattern as determined with external beam proton-induced X-ray emission, with hotspots of Cu and S appearing in the hilum and micropyle area that indicated a possible uptake mechanism via the seed coat. The nano-digenite also triggered a plant stress response by slightly altering seed amino acid metabolism. Ultimately, the nano-digenite may have important implications as a seed protective or nutritive agent as advised by its unique distribution pattern and effect on amino acid metabolism.

Graphical abstract

graphic file with name 11671_2023_3953_Figa_HTML.jpg

Keywords: Amino acid, Avocado-seed-extract, CuS, Nanofertilizer, Phaseolus vulgaris

Introduction

Climate change, an ever-increasing global population demanding high quality food, soaring food costs due to fertilizer shortages, and the adverse impact of the augmented application of chemical and organic fertilizers on the environment and soil fertility collectively support the urgent need to develop sustainable agricultural technologies that can revolutionize crop productivity and quality [1, 2]. To address these broad-based challenges, the development and utilisation of so-called nanotechnology-enabled fertilizers or nanofertilizers to substitute traditional agrochemicals, have presented with significant prospects in research and agriculture due to their unique physico-chemical make-up, nano-size dimensions, and high area to volume ratio facilitating enhanced nutrient use efficiency [3]. A variety of studies on seeds and seedling activity of metal-oxide (e.g. MoO, CeO2, CuO, TiO2, and ZnO) [4–6] and metal sulphide (e.g. MoS, Ag2S, ZnS, FeS, MnS) [4, 7–10] nanoparticles has been done and showed that metal based nanoparticles impact on plant growth vary based on the type, size, shape, concentration and seed/plant species. In contradictory, it has currently been noted that nanoparticle synthesis and test methods also have an influence on the development of the plant [11]. Some nanoparticles have shown no influence at all, a study on molybdenum oxide and sulphide nanoparticles showed that the growth of Oryza sativa L. was not improved by 100 ppm concentrations of the nanoparticles [4].

A growing number of studies on uptake and seedling activity of particles are focusing on utilizing metal-based nanoparticles such as copper-sulphur-based nano fertilizers to enhance plant nutrition and growth due to their unique effect on plant metabolic activities, crop resilience to pathogens, and survival of plants under abiotic stress [12–14]. However, reports focused on the effect of Phyto engineered CuS nano fertilizers on plant physiology are lacking. Biogenic metallic nanoparticles developed using Phyto engineering presents as an eco-friendlier, energy efficient, economical, and timeous one-pot synthesis approach towards the large-scale production of highly biocompatible and multifunctional nanoparticles that have been shown to have unique Physico-chemical properties in terms of size, shape, composition, surface functional chemistry, and chemical stability that may have unique benefits to plants [15–20]. Furthermore, although the interaction between different plant phytochemical compounds and nanoparticles plays a critical role in phyto-engineering a product with unique properties, computational studies delineating the interaction between the plant materials used in Phyto engineering and the nanoparticle surface are lacking for metal-based nanofertilizers.

Although nanofertilizers have been applied as foliar or soil nutrition, seed priming with metal-based nanofertilizers presents with added advantages since its application can be performed at one of the most important stages of a plant’s life cycle and under controlled conditions [21–23]. Ultimately, seed nanopriming with green synthesized metal-based nanofertilizers may present as an eco-friendlier approach to applying more bioeffective fertilizers [24]. Seed priming studies with nanofertilizers have shown that nanofertilizers have a multifaceted effect on seed physiology [21] However, most metal or Cu-based nanofertilizer studies have mainly focused on seed physiology in terms of water uptake and germination parameters such as germination time and rate combined with other plant physiological parameters [25]. Essentially, nothing is known about the fundamental interaction of green synthesized CuS-based nanofertilizers with seeds in terms of its effect on amino acid metabolism which may well reflect the plant’s stress response metabolism to the application of a non-traditional fertilizer. Furthermore, nothing is known about the distribution of nanofertilizers in seed morphological regions that may have important implications for seed protection and nutrition.

The aim of this study was to screen the interaction of phytoengineered CuS nanoparticles with Pinto beans (Phaseolus vulgaris L.) as bean crops serve as a nutritional security cash crop that has a lower carbon footprint, energy consumption, land and water use [26, 27]. We describe here (1) the molecular dynamics simulation [28–33]; motivated phytoengineering of CuS nanoparticles (2) their distribution inside seeds morphological regions and effect on the seed ionome using external beam proton induced X-ray emission; and (3) their effect on amino acid metabolism.

Experimental

Preparation of avocado aqueous extract and nanoparticle

To prepare the aqueous avocado seed extract, the seeds collected from waste were washed with DI water and grated with a blender to obtain the seed powder which was dried overnight in an oven at 50 °C. An aqueous solution of avocado seed extract was prepared as previously described [34]. CuS nanoparticles were prepared by modifying a previously reported method [35]. The dried powder was annealed under vacuum at 400 °C for 2 h to obtain CuS nanoparticles.

Preparation of imbibing solutions and seed imbibing

The nanoparticle solution was freshly prepared at a concentration of 0.3 mg/ml [36] by dispersing the nanoparticles in DI water using ultrasonic vibration (100 w, 40 kHz) for 30 min. Only deionized water was used for the control treatment. Healthy Pinto bean seeds that represented one cultivar were obtained from Seeds for Africa (Rivergate Industrial, Cape Farms, South Africa) and healthy seeds selected from the same seed lot and used for all the experiments. The seeds were rinsed several times with DI water and immediately soaked for 24 h with continuous aeration in the nanofertilizer solution at a concentration of 0.3 mg/ml and seed weight: solution volume of 1:4 gmL−1.

External beam PIXE analysis

The area on all samples was subsequently measured with a proton beam (spot size = 50 µm) of an initial energy of 3 MeV that decreased to approximately to 2.98 MeV on the target due to energy loss in the exit window of 200 nm Si3N4 and air gap of 4 mm. All samples were measured with an ion current of 1–3 nA. Typically, about 10.000 points were selected for each map and the dwelling time in particular point was 3–4 s. The energy range of the detected X-rays was set between 1.5 and 30 keV. Emitted X-rays were detected by a Si (Li) detector (resolution, 145 eV at 5.89 keV, 4.3 cm from target, 135° angle to the beam direction). Apart from the air space between the sample and detector, the X-rays passed a pinhole (funny) filter of 50 μm aluminium foil (relative opening, 10%) to balance the intense peaks of light elements and low intensity peaks of metal elements. The transmission function was carefully measured and fitted to an analytical function. The spectra were normalized according to the signal from the chopper that intersected the beam in vacuum. The measured quantity included the RBS signal from the gold foil mounted on chopper wings. The spectral fitting was performed by the Xantho code and elemental concentrations were determined according to the instrumental constants that was determined from the measurement on NIST 620 standard glass. For test measurements, we measured the tomato leaves standard NIST 1573a as an unknown target, whilst for the analysis of bean seeds the analysed elements were assumed to be imbedded in a cellulose matrix.

Seed amino acid extraction and quantification

The seeds were frozen in liquid nitrogen using a liquid nitrogen pre-chilled pestle and mortar and ground to a fine powder. The method for amino acid extraction and analysis was completed as described in [37]. After imbibition, the dry weight of the samples was recorded. The seeds were subsequently frozen in liquid nitrogen using a liquid nitrogen pre-chilled pestle and mortar and ground to a fine powder after the liquid nitrogen had evaporated. A 0.5 ml solution containing 6 M of HCl with Norleucine (250 ppm) as the internal standard was added to the dried seed powder for protein hydrolysis. AccQ-Tag derivates of amino acids were extracted using an AccQ-Tag Ultra Derivatization Kit according to the manufacturer’s instructions (Waters). A Waters Acquity Ultra Performance Liquid Chromatograph system equipped with a photodiode array detector (260 nm), binary solvent delivery system, and an auto sampler was used to analyze the derivatized amino acids. The sample/standard solution (1 µL) was injected into the mobile phase, which conveyed derivatised amino acids onto a Waters AccQ-Tag Ultra C18 column (2.1 × 1000 mm × 1.7 µm) maintained at 60 °C for separation. Amino acids in the samples were identified by co-elution with an amino acid standard H (Pierce) and commercially available individual amino acids (Sigma). Instrument control and data acquisition was performed by MassLynx software which integrates the peaks at the defined retention times and plots calibration curves for each amino acid based on the peak response (peak area/internal standard peak area) against concentration.

Molecular dynamics simulation

The molecular dynamics simulations were conducted using GROMACS 2019 software [30, 31, 38], employing periodic boundary conditions along with the CHARMM36 force field [32, 39] and the SPC water model [40]. Additionally, the TIP3P model was utilized for the water molecules within the complex [31, 34]. The energy of the systems was optimized using the steepest descent algorithm for all atoms [41]. The NVT ensemble (constant number of particles (N), volume (V), and temperature (T)) coupled to the V-rescale thermal bath at 300 K for 200 ps and the NPT ensemble coupled to the Berendsen pressure bath at 1 atm for 300 ps were used to equilibrate each system. Subsequently, each system was subjected to a 50 ns molecular dynamics simulation with a time step of 1 fs and constant conditions of 1 atm and 300 K. The H-bond lengths were constrained using the LINCS algorithm [42]. Long-range electrostatics were applied using the particle mesh Ewald [43] method. The trajectory data was analyzed using GROMACS utilities, and molecular graphics and visualizations were created using VMD 1.9.3 [44]. CHARMM CGenFF [45] was used to calculate the force fields of CuS and compounds. Six active compounds (4-hydroxybenzoic acid, citric acid, protocatechuic acid, pyrocatechol, quinic acid, and succinic acid) had their electronic structures determined using the Gaussian program, version 09 [46]. The geometry of the molecules was optimized at the B3LYP/6–311++g (d, p) level of theory.

Statistical analyses

All the analysis were performed in triplicate. For the amino acid data, the data were summarized using summative statistics and an empirical approach used. An unpaired t-test was further used to compare means with significance set at p < 0.05. Secondary statistical analysis was performed using a heatmap as previously described [47] and as both a visualization and partitioning tool for the amino acid metabolome data.

Results and discussion

Characterization of CuS nanoparticles

The TEM image (Fig. 1a) at 50 nm scale shows the shape of the particles to be a mixture of spherical and semi spherical with some degree of agglomeration, with an average size of 77.89 nm as shown by the histogram (Fig. 1b). SEM image (Fig. 1c) shows that the synthesised CuS nanoparticles have a rough surface morphology that matches with the previously described CuS nanoparticles [48]. EDX (Fig. 1d) detected carbon, nitrogen and oxygen which could originate from phytocompounds in the avocado seed extract [49], with the presence of Cu and S confirming the formation of the CuS nanoparticles. The presence of phytochemicals such as phenols, alcohols, amines, and carboxylic acid that are known to be present in avocado seeds were further confirmed by comparing the avocado seed powder to the CuS nanoparticle FTIR spectrum (Fig. 1e), both spectra show almost identical vibration peaks [50]. One peak at 694 cm−1 from the avocado seed split into two peaks in the CuS and appeared at 769 and 688 cm−1 confirming the incorporation of CuS into the chemical structure. XRD in Fig. 1f shows no diffraction peaks associated with impurities, However, only pure digenite (Cu9S5) phase obtained in reference to JCPDS Cards No. 00-047-1748. The diffraction peaks obtained matched the diffraction peaks obtained in the literature [51]. The Debye–Scherrer equation (D = kλ/βCosθ) was employed to calculate the average size of the Cu9S5 nanoparticles from the most intense peak to be 70 nm [52, 53].

Fig. 1.

Fig. 1

a TEM image, b size distribution histogram, c SEM image d EDS spectra, e FTIR spectra, and f XRD Patterns of CuS nanoparticles

External beam PIXE analysis

Figures 2 and 3 presents the elemental maps of Cu, Zn, Fe, S, K, and Ca distribution intensity obtained from cross-sectioned beans representing nanofertilizer imbibed and control samples imbibed with only deionized water and corresponding semi-quantitative line scan maps across the seed morphological regions, respectively. Some maps, i.e., those of Cu and Fe in the control samples presenting with lower counting statistics and less visually convincing results, were also included since it consistently showed dissimilar distribution patterns between test and control samples. The analysis revealed that the elemental distribution patterns differed between treated and control samples in terms of distribution and intensity and that specific elements tended to accumulate in specific seed morphological regions. For example, in treated samples, Cu was mainly accumulated within the micropyle, hilum, and seed coat regions; Zn, Fe, and Ca were more concentrated in the seed coat region; S showed hotspots in the seed coat close to the hilum and micropyle regions like Cu; and K accumulated within the cotyledon. In control samples, Zn distribution seemed more prominent in the seed coat, S showed some hotspots in the testa and seed coat regions, whilst Ca was mainly located within the seed coat regions. For K, higher intensities were noted within the testa and seed coat regions. Overall, K, Cu, S, and Zn showed notable variation in distribution and intensity patterns between control and treated samples.

Fig. 2.

Fig. 2

Elemental distribution maps of Cu, Zn, Fe, S, K, and Ca in CuS nanofertilizer treated and control Pinto bean (Phaseolus vulgaris L.) seeds treated with water. The intensity scale emphasizes certain elemental distribution features

Fig. 3.

Fig. 3

Fig. 3

Semi-quantitative (in weight percentage) line scans performed for areas marked in green (A) and blue (B) linked to different seed morphological regions. The top image presents control Pinto bean (Phaseolus vulgaris L.) seeds treated with water, whilst the bottom image represents nanofertilizer treated Pinto bean seeds, The line scans confirm that Cu, Zn, Fe and Ca were mostly accumulated within the seed coat regions, whereas K accumulated within the cotelydon region

The results of the elemental mapping data agree with the study [46] on the localization of chemically synthesized and coated iron oxide nanoparticles in tomato seeds. For beans, previous studies have also shown that, depending on the bean cultivar, Cu, Zn, Fe, and Ca are mainly localized within the seed coat, whereas K tend to accumulate more within the internal seed regions [27]. The distribution patterns observed here may be ascribed to a physiological mechanism whereby bean seeds store specific elements within specific morphological regions [54]. For example, Ca has been shown to have restricted movement between the seed coat and embryo due to the presence of insoluble calcium oxalate crystals in the mature seed coat [27, 55]. Specific elements may also have a biological function linked to a specific seed morphological region [56], whilst seed chemistry may likewise play a significant role as seed coat tannins or other biocompounds such as amino acids may complex metal containing compounds [27, 57]. Ultimately, differences in the intensity and distribution patterns for Cu, Zn, Fe, S, and K between the treatments could be ascribed to the effect of the nanofertilizer on the intricate physiological and metabolic mechanisms governing uptake, distribution, and storage of elements in seeds. More specifically, the distinct distribution patterns for K between test and control samples could be ascribed to the binding of Cu ions to metallothionein proteins in the seed embryonic region [58] which may impact the activity of phytases [59]. The end products of phytate breakdown may in turn affect the activity of K channels which mediates K transport between seed morphological regions [60]. Alternatively, the distribution pattern and dynamics of K movement could be a response to the seed’s multistage hydration dynamics mediated by the nanofertilizer [61], beginning at the micropyle and hilum and filling the voids between the cotyledons and seed coat [62, 63].

Interestingly, the CuS nanofertilizer were mainly accumulated within the seed coat area that supports previous studies showing that nanofertilizers mainly accumulate within this area [64]. More specifically, the nanofertilizer showed hotspots within the hilum and micropyle regions that act as a hygroscopic valve responsible for water uptake. On a microlevel nanofertilizers may bind to carrier proteins, ion channels, or membrane transporters [65]. It has also been hypothesized that nanofertilizers may enter plant material via intercellular spaces, pore size enlargement, the induction of new cell wall nanopores, or via endocytosis [66–68]. The creation of nanopores may further upregulate aquaporin production and water uptake [67], hence facilitating the entry of an aqueous nanofertilizer solution into the seed [69, 70]. Alternatively, the nanoparticles forming part of the nanofertilzer may attach to and create nanopores within the spongy like and stacked tissue layers of the hilum containing branched, dead tracheid cells with lignified cell walls [71].

Other than the multifaceted chemistry, physiology, homeostasis, and metabolism of the plant region exposed to the nanofertilizer, the physico-chemical properties, i.e. size, morphology, chemical composition, surface functionalization, and concentration of the individual nanoparticles that constitute the nanofertilizer may also have a multidimensional effect on nanofertilizer uptake [67, 72]. Here, the functionalization and coating of the nanofertilizer [53] or its low solubility [73] that may serve as a barrier to transport into the seed cotyledon, may further explain restriction of the nanofertilizer to the seed coat area.

Nevertheless, although the interaction between nanofertilizers and the seed coat is generally poorly explored, the presence of the CuS nanofertilizer in the seed coat region presents with significance. Since the seed coat is responsible for protecting the internal seed regions against biotic and abiotic onslaughts [70, 74], accumulation of a Cu-based nanofertilizer in this region may potentially act as a barrier to infective agents such as fungi due to the antimicrobial properties of metal nanoparticles [75]. Furthermore, since the nanofertilizer accumulated in the seed coat, its application may present as versatile carrier platform for not only seed pest control, but also to deliver nutrients or growth factor agents during the early stages of plant development [53]. Interestingly, the seed coat also acts as a channel transmitting cues about the external environment [76]. To illustrate, external nutrients in the form of a nanofertilizer that may eventually pass the seed coat to the internal seed regions to initiate seed development may also trigger downstream macromolecular responses to alter seed metabolism in response to external environment changes [77].

Amino acid profiling

Nanofertilizer treated and control seeds were analyzed for 16 essential and non-essential amino acids. The mean ± SD of amino acid content in treated versus control seeds are presented in Fig. 4a. Descriptive statistical analysis showed that some of the amino acids were slightly upregulated in treated seeds, whilst others were slightly downregulated. Phenylalanine showed the highest increase of 20%, whilst lysine showed the highest decrease of 20% between test and control samples. No significant differences (p > 0.05) were noted for amino acid levels between the treatments.

Fig. 4.

Fig. 4

Doughnut graph a depicting amino acid levels between CuS nanofertilizer treated Pinto bean seeds (inner doughnut chart) and seeds treated with only water (control, outer doughnut chart). Values in the chart are expressed as mean ± SD % g/100 g dry weight of samples. b presents a heatmap generated using complete linkage hierarchical clustering based on Euclidean distances showing the median amino acid abundances (quantified as moderated z-scores) of clusters for amino acid compositions of Pinto bean seeds treated with CuS nanofertilizer and control seeds treated with only water. The relationship is presented by a dendrogram in which rows represent treatment and columns amino acid content, with a specific colour representing the magnitude of abundance (please refer to the text for a full explanation of the heatmap results)

Secondary statistical analysis with hierarchical clustering showed the similarities and differences in the amino acid contents based on individual treatments and the similarity or differences between individual treatments based on amino acid contents. The colour legend of the heatmap (Fig. 4b) indicates a lower average amino acid concentration (blue) or a higher average amino acid concentration (red) in a particular sample. The nanofertilizer treated seeds were differentiated from and showed the highest dissimilarity (as shown by the brightest colours of the colour map) to the control treatment by more extreme z-scores in the negative or below average and positive or above average direction for specific subsets of amino acids compared to the control treatment. Interestingly, isoleucine, alanine, and methionine formed a separate cluster with the rest of the amino acids that formed part of a bigger cluster. This clustering pattern could be linked to the multifunctional interaction of the amino acid groups related to their unique chemistry and physiological roles [78, 79]. Collectively, the heatmap results support and build on the summative statistical analysis.

In sum, it has been shown that metal nanoparticles trigger changes in biochemical reactions by for example downregulating or upregulating metabolites such as amino acids that may affect the plant’s adaptive reaction to changing environmental conditions [80, 81]. Quantitative determination of amino acids is hence important in mapping the metabolome response to environmental cues. Of the amino acids, lysine and phenylalanine showed the most marked response between treatments. Lysine—a nutritionally essential amino acid that at high concentrations may retard germination—was downregulated in test versus control samples [82]. Phenylalanine representing a non-essential amino acid and involved in the defence system of a plant [83, 84] was however upregulated in test versus control samples, although not at a significant level. Furthermore, glutamic acid that plays a significant role in nitrogen metabolism, amino acid and protein synthesis, and the synthesis of phytochelating agents known for binding metals [85, 86] was slightly upregulated together with arginine that also serves as an important nitrogen reserve and precursor for the biosynthesis of polyamines and nitric oxide which regulates nutrient uptake and activates disease and stress tolerance mechanisms in plants [87]. Tyrosine that serves as a precursor of various specialized metabolites such as electron carriers, antioxidants, and defence compounds was also slightly upregulated [88]. Only aspartic acid which serves as a central building block in nitrogen and carbon metabolism and biosynthesis of other amino acids, nucleotides, organic acids, sugars, and other compounds vital for plant growth and stress resistance [89] was slightly downregulated in addition to isoleucine that is known to play a role in plant stress resistance as an osmo-regulation factor [90].

Molecular dynamics simulation

Figure 5 illustrates the charge distribution and electrostatic potential maps of six active compounds, highlighting their active interaction sites with the nanoparticle surface. We derived the Hirshfeld point charges and electrostatic potentials for these compounds' optimized structures through density functional theory, using water as a solvent. The most intense red regions in these maps indicate where the molecules are most likely to interact with the nanoparticle. Specifically, the atoms with the strongest attraction to the CuS surface are O3 in 4-hydroxybenzoic acid, O6 in citric acid, O4 in protocatechuic acid, O1 in pyrocatechol, O3 in quinic acid, and O3/O4 in succinic acid.

Fig. 5.

Fig. 5

Charge distribution (Hirshfeld point charges) and electrostatic potential map of a 4-hydroxybenzoic acid, b citric acid, c protocatechuic acid, d pyrocatechol, e quinic acid, and f succinic acid. The geometry optimization of active compounds was carried out at the B3LYP/6–311++g(d,p) level of theory

As depicted in Fig. 6, the g(r) has a maximum peak for the atoms O3 in 4-hydroxybenzoic acid, O6 in citric acid, O4 in protocatechuic acid, O1 in pyrocatechol, O3 in quinic acid and succinic acid, which exhibit the highest affinity to interact with the nanoparticle compared to other types of oxygen and carbon atoms, as was determined by DFT calculations as well.

Fig. 6.

Fig. 6

Radial distribution function plots for the active sites of a 4-hydroxybenzoic acid, b citric acid, c protocatechuic acid, d pyrocatechol, e quinic acid, and f succinic acid with respect to the surface of CuS nanoparticle

LogS is a logarithmic measure of a molecule’s solubility in water, expressed as the base-10 log of its solubility in moles per liter. This metric is a reliable indicator of a compound’s hydrophilicity. Specifically, LogS values above − 1 signify a molecule’s high polarity and affinity for water [91]. Moreover, molecules with LogS values ranging from − 1 to − 5 exhibit a balanced profile of water-solubility and lipophilicity, enabling them to associate with hydrophobic entities [91, 92]. Utilizing Playground v1.5.0 software, the LogS values for various compounds were calculated to assess their solubility in water [93]. The outcomes revealed that 4-hydroxybenzoic acid has the lowest solubility with a LogS value of − 1.07. This is followed by increased solubility in protocatechuic acid (− 0.68), pyrocatechol (− 0.52), and even higher solubility in quinic acid (0.16), citric acid (0.40), and succinic acid (0.77), in ascending order.

Figure 7 illustrates that 4-Hydroxybenzoic acid exhibits the most pronounced peak in the radial distribution function (g(r)) at approximately 2.5 Å from the nanoparticle's surface, suggesting a strong affinity for interaction despite its relatively low solubility (logS value). In contrast, succinic acid, which displays the smallest g(r) peak, shows a lower propensity to interact with the nanoparticle surface, correlating with its high logS value, indicative of greater solubility. Additionally, when analyzing the interaction energies, which combine Van der Waals and electrostatic potential energies, a trend emerges: the interaction energy is higher near the surface of CuS for the 4-Hydroxybenzoic acid than other compounds in an aqueous environment. The data from interaction energies and the radial distribution function (RDF) graphs, as presented in Fig. 6, corroborate the logS values’ implications. They collectively suggest that succinic acid is markedly more hydrophilic compared to other active compounds, thereby preferring interaction with water molecules over the nanoparticle surface.

Fig. 7.

Fig. 7

The radial distribution function plots illustrate the spatial distribution of six active compounds in relation to the CuS surface

Conclusions

To promote our understanding for the rational use of nanotechnology for seed treatment in agriculture, this study presents the first report applying computational modelling supported Phyto engineered CuS nanoparticles as a seed imbibing agent to study its effect on the distribution of elements across different seed morphological regions combined with its effect on the amino acid metabolome using both benchtop and ion beam techniques. Molecular dynamics simulations showed that specific phytocompounds had a higher affinity for interacting with the nanoparticle's surface than other active compounds. The nanofertilizer containing nanoparticles of ca. 77 nm were retained within the seed coat region which generally serves as a barrier for seed protection, nutrient reserve, and response trigger to a changing environment [80]. Although the reasons supporting the preferential and more intense elemental accumulation patterns triggered by the nanofertilizer for some elements are unclear, the intricate crosstalk between the chemico-physiology of the bean regions with the unique Physico-chemical properties of the nanofertilizer as characterized by physico-chemical analyses and computational modelling may play a significant role. The unique changes in the ionome in terms of its distribution between treated and control seeds may have triggered a secondary metabolite response in the form of amino acid level changes, with the slight change observed in amino acid levels not sufficient to indicate a strong plant defence mechanism. Regardless, the fact that the nanofertilizer accumulated within the seed coat regions may have significant implications for the use of this nanofertilizer as a versatile carrier technology to deliver nutrients or antimicrobials [72]. In future, laboratory studies as here described are firstly warranted before applied studies in the field can be executed to screen the growth physiology and performance of seeds treated with nanofertilizers as affected by a host of soil Physico-chemistry and environmental factors. For example, answering fundamental questions is first and foremost important, such as the distribution of the nanofertilizer within seed morphological regions that may also affect for example its seed antimicrobial potential, whilst activation or changes in amino acid metabolism by the nanofertilizer may further serve to improve the resilience of the seed to abiotic and biotic stress.

Acknowledgements

The authors acknowledge the Centre for High Performance Computing, South Africa, for providing computational resources and facilities for this research, University of South Africa and iThemba labs (NRF) and University of the Western Cape School of Pharmacy. Luis P. M. Santos thanks CAPES for his scholarship (88882.463158/2019-01) PNPD/CAPES

Author contributions

For the manuscript entitled: “Molecular dynamics simulation and elemental mapping of phyto-engineered digenite nanoparticles interaction with Pinto bean (Phaseolus vulgaris L.) seeds and its effect on the seed elemental and amino acid profile” by N.L.B., K.J.C., M.A., R.M., C.K., N.M., R.B., and M.M. Contributions are as follows: N.L.B. and K.J.C. performed the lab work and wrote the manuscript, M.A and R.M performed the computational studies, I.M. performed the annealing of the material, A.D. and O.M.D performed the antibacterial studies, Z.S, K.I, P.P. and K.J.C. performed the sample preparation and ion beam analysis, L.P.M.S did the XRD analysis of the material, and M.M and K.J.C. supervised the work and was in charge of the acquisition of funding and resources.

Funding

The research leading to this result has been supported by the RADIATE project under the Grant Agreement 824096 from the EU Research and Innovation programme HORIZON 2020.

Data availability

The data supporting the findings reported is available upon reasonable request from the corresponding author.

Declarations

Ethics approval and consent to participate

This study used avocado seed that was collected from waste. All methods were carried out in accordance with relevant guidelines and regulations. No consent or approval / licences were required.

Consent for publication

Not applicable.

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

Nandipha L. Botha, Email: bothanandipha9@gmail.com

Karen J. Cloete, Email: kaboutercloete@gmail.com

References

  • 1.Raliya R, Saharan V, Dimkpa C, Biswas P. Nanofertilizer for precision and sustainable agriculture: current state and future perspectives. J Agric Food Chem. 2015;66(26):6487–6503. doi: 10.1021/acs.jafc.7b02178. [DOI] [PubMed] [Google Scholar]
  • 2.Fatima F, Hashim A, Anees S. Efficacy of nanoparticles as nanofertilizer production: a review. Environ Sci Pollut Res. 2021 doi: 10.1007/s11356-020-11218-9. [DOI] [PubMed] [Google Scholar]
  • 3.Jakhar A, Aziz I, Kaleri AR, Hasnain M, Haider G, Ma J, Abideen Z. Nano-fertilizers: a sustainable technology for improving crop nutrition and food security. NanoImpact. 2022;27:100411. doi: 10.1016/j.impact.2022.100411. [DOI] [PubMed] [Google Scholar]
  • 4.Sharma PK, Raghubanshi AS, Shah K. Examining the uptake and bioaccumulation of molybdenum nanoparticles and their effect on antioxidant activities in growing rice seedlings. Environ Sci Pollut Res. 2021;28:13439–13453. doi: 10.1007/s11356-020-11511-7. [DOI] [PubMed] [Google Scholar]
  • 5.Khepar V, Ahuja R, Sidhu A, SamotaM K. Nano-sulfides of Fe and Mn efficiently augmented the growth, antioxidant defense system, and metal assimilation in rice seedlings. ACS Omega. 2023;8(33):30231–30238. doi: 10.1021/acsomega.3c03012. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 6.Ahuja R, Sidhu A, Bala A. Synthesis, and evaluation of iron(ii) sulfide aqua nanoparticles (FeS-NPs) against Fusarium verticillioides causing sheath rot and seed discoloration of rice. Eur J Plant Pathol. 2019;155:163–171. doi: 10.1007/s10658-019-01758-3. [DOI] [Google Scholar]
  • 7.Afsheen S, Naseer H, Iqbal T, Abrar M, Bashir A, Ijaz M. Synthesis, and characterization of metal sulphide nanoparticles to investigate the effect of nanoparticles on germination of soybean and wheat seeds. Mater Chem Phys. 2020;252:123216. doi: 10.1016/j.matchemphys.2020.123216. [DOI] [Google Scholar]
  • 8.Wang P, Menzies NW, Lombi E, Sekine R, Blamey FPC, Hernandez-Soriano MC, Cheng M, Kappen P, Peijnenburg WJGM, Tang C, Kopittke PM. Silver sulfide nanoparticles (Ag2S-NPs) are taken up by plants and are phytotoxic. Nanotoxicology. 2015;9(8):1041–1049. doi: 10.3109/17435390.2014.999139. [DOI] [PubMed] [Google Scholar]
  • 9.Rizwan M, Ali S, Qayyum MF, Ok YS, Adrees M, Ibrahim M, Zia-ur-Rehman M, Farid M, Abbas F. Effect of metal and metal oxide nanoparticles on growth and physiology of globally important food crops: a critical review. J Hazard Mater. 2017;322(Part A):2–16. doi: 10.1016/j.jhazmat.2016.05.061. [DOI] [PubMed] [Google Scholar]
  • 10.Du W, Tan W, Peralta-Videa JR, Gardea-Torresdey JL, Ji R, Yin Y, Guo H. Interaction of metal oxide nanoparticles with higher terrestrial plants: physiological and biochemical aspects. Plant Physiol Biochem. 2017;110:210–225. doi: 10.1016/j.plaphy.2016.04.024. [DOI] [PubMed] [Google Scholar]
  • 11.García-Gómez C, Fernández MD. Chapter four—impacts of metal oxide nanoparticles on seed germination, plant growth and development. Compr Anal Chem. 2019;84:75–124. doi: 10.1016/bs.coac.2019.04.007. [DOI] [Google Scholar]
  • 12.Liu W, Zeb A, Lian J, Wu J, Xiong H, Tang J, Zheng S. Interactions of metal-based and metal-oxide-based nanoparticles (MBNPs and MONPs) with crop plants: a critical review of research progress and prospects. Environ Rev. 2020;28:294–310. doi: 10.1139/er-2019-0085. [DOI] [Google Scholar]
  • 13.Tripathi R, Tewari R, Singh KP, Keswani C, Minkina T, Srivastava AK, De Corato U, Sansinenea E. Plant mineral nutrition and disease resistance: a significant linkage for sustainable crop protection. Front Plant Sci. 2022;13:883970. doi: 10.3389/fpls.2022.883970. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Abou Seeda MA, Abou El-Nour EAA, Yassen AA, Gad Mervat M, Zaghloul SM. Importance of sulfur and its roles in plants physiology: a review. Curr Sci Int. 2020;09(02):198–231. [Google Scholar]
  • 15.Madani M, Hosny SA, Dalal M, Nady NA, Sheikha A, Alkhaldi H, Al-Gahtany SAG, Mohamed M, Gaber GA. Green synthesis of nanoparticles for varied applications: green renewable resources and energy-efficient synthetic routes. Nanotechnol Rev. 2022;11(1):731–759. doi: 10.1515/ntrev-2022-0034. [DOI] [Google Scholar]
  • 16.Jadoun S, Arif R, Jangid NK, et al. Green synthesis of nanoparticles using plant extracts: a review. Environ Chem Lett. 2021;19:355–374. doi: 10.1007/s10311-020-01074-x. [DOI] [Google Scholar]
  • 17.Chetan P, Arpita R, Suresh G, Ameer K, Mohammad NI, Talha BE, Siok EL, Mayeen UK, David AB. Biological agents for synthesis of nanoparticles and their applications. J. King Saud Univ Sci. 2022;34(3):101869. doi: 10.1016/j.jksus.2022.101869. [DOI] [Google Scholar]
  • 18.Singh J, Dutta T, Kim KH, et al. ‘Green’ synthesis of metals and their oxide nanoparticles: applications for environmental remediation. J Nanobiotechnol. 2018;16:84. doi: 10.1186/s12951-018-0408-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Saravanan A. A review on biosynthesis of metal nanoparticles and its environmental applications. Chemosphere. 2011;264:128580. doi: 10.1016/j.chemosphere.2020.128580. [DOI] [PubMed] [Google Scholar]
  • 20.García-Ovando AE, Ramírez Piña JE, Esquivel Naranjo EU, Cervantes Chávez JA, Esquivel K. Biosynthesized nanoparticles, and implications by their use in crops: effects over physiology, action mechanisms, plant stress responses and toxicity. Plant Stress. 2022;6:100109. doi: 10.1016/j.stress.2022.100109. [DOI] [Google Scholar]
  • 21.Nile SH, Thiruvengadam M, Wang Y, et al. Nano-priming as emerging seed priming technology for sustainable agriculture—recent developments and future perspectives. J Nanobiotechnol. 2020;20:254. doi: 10.1186/s12951-022-01423-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.Shukla P, Chaurasia P, Younis K, Qadri O, Faridi S, Srivastava G. Nanotechnology in sustainable agriculture: studies from seed priming to post-harvest management. Nanotechnol Environ Eng. 2019;4:1–15. doi: 10.1007/s41204-019-0058-2. [DOI] [Google Scholar]
  • 23.Santo Pereira EA, Oliveira CH, Fraceto FL, Santaella C. Nanotechnology potential in seed priming for sustainable agriculture. Nanomaterials. 2021;11(2):267. doi: 10.3390/nano11020267. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 24.Raja K, Sowmya R, Sudhagar R, Moorthy S, Govindaraju K, Subramanian KS. Biogenic ZnO and Cu nanoparticles to improve seed germination quality in black gram (Vigna mungo) Mat Lett. 2019;235:164–167. doi: 10.1016/j.matlet.2018.10.038. [DOI] [Google Scholar]
  • 25.Hussain M, Raja NI, Zia-Ur-Rehman M, Iqbal M, Ejaz M, Yasmeen SF. In vitro germination and biochemical profiling of citrus reticulata in response to green synthesised zinc and copper nanoparticles. ET Nanobiotechnol. 2017;11(7):790–796. doi: 10.1049/iet-nbt.2016.0256. [DOI] [Google Scholar]
  • 26.Uebersax M, Cichy KA, Gomez FE, Porch TG, Heitholt J, Osorno JM, Kamfwa K, Snapp SS, Bales S. Dry beans (Phaseolus vulgaris L.) as a vital component of sustainable agriculture and food security—a review. Legume Sci. 2022;5:e155. doi: 10.1002/leg3.155. [DOI] [Google Scholar]
  • 27.Ribeiro ND, Maziero SM, Prigol M, Nogueira CW, Rosa DP, Possobom MTDF. Mineral concentrations in the embryo and seed coat of common bean cultivars. J Food Compos Anal. 2012;26(1–2):89–95. doi: 10.1016/j.jfca.2012.03.003. [DOI] [Google Scholar]
  • 28.Morad R, Akbari M, Rezaee P, Koochaki A, Maaz M, Jamshidi Z. First principal simulation of coated hydroxychloroquine on Ag, Au and Pt nanoparticles. Sci Rep. 2021;11:2131. doi: 10.1038/s41598-021-81617-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 29.Akbari M, Morad R, Maaza M. First principal study of silver nanoparticle interactions with antimalarial drugs extracted from Artemisia annua plant. J Nanopart Res. 2020;22(11):1–9. doi: 10.1007/s11051-020-05058-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30.Sackey J, Akbari M, Morad R, Bashir AKH, Ndiaye NM, Matinise N, Maaza M. Molecular dynamics, and biosynthesis of phoenix dactylifera mediated Mn3O4 nanoparticles: electrochemical application. J Alloys Compd. 2020;854:156987. doi: 10.1016/j.jallcom.2020.156987. [DOI] [Google Scholar]
  • 31.Sackey J, Akbari M, Tandjigora N, Cloete KJ, Bashir AKH, Morad R, Maaza M. Industrial textile removal using date pit assisted CuO–MgO nanocomposite: molecular dynamics and biosynthesis analysis. J King Saud Univ-Sci. 2022;34(3):101840. doi: 10.1016/j.jksus.2022.101840. [DOI] [Google Scholar]
  • 32.Akbari M, Morad R, Maaza M. Effect of silver nanoparticle size on interaction with artemisinin: first principle study. Results Surfaces Interfaces. 2023;11:100104. doi: 10.1016/j.rsurfi.2023.100104. [DOI] [Google Scholar]
  • 33.Shafiee Z, Karami L, Akbari M, Rezaee E, Maaza M, Tabatabai SA, Karimi G. Insights into the molecular mechanism of triazolopyrimidinone derivatives effects on the modulation of α1β2γ2 subtype of GABAA receptor: an in-silico approach. Arch Biochem Biophys. 2022;729:109380. doi: 10.1016/j.abb.2022.109380. [DOI] [PubMed] [Google Scholar]
  • 34.Botha NL, Cloete KJ, Welegergs GG, Akbari M, Morad R, Kotsedi L, Matinise N, Bucher N, Azizi S, Maaza M. Physical properties of computationally informed phyto-engineered 2-D nanoscaled hydronium jarosite. Sci Rep. 2023;13:2442. doi: 10.1038/s41598-022-25723-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 35.Saranya M, Santhosh C, Augustine SP, Grace AN. Synthesis, and characterisation of CuS nanomaterials using hydrothermal route. J Exp Nanosci. 2014;9:329–336. doi: 10.1080/17458080.2012.661471. [DOI] [Google Scholar]
  • 36.Nair PM, Chung IM. A mechanistic study on the toxic effect of copper oxide nanoparticles in soybean (Glycine max L.) root development and lignifcation of root cells. Biol Trace Elem Res. 2014;162(1–3):342–352. doi: 10.1007/s12011-014-0106-5. [DOI] [PubMed] [Google Scholar]
  • 37.Mncwangi NP, Viljoen AM. Quantitative variation of amino acids in Sutherlandia frutescens (Cancer bush)—towards setting parameters for quality control. S Afr J Bot. 2012;82:46–52. doi: 10.1016/j.sajb.2012.06.009. [DOI] [Google Scholar]
  • 38.Abraham MJ, van der Spoel D, Lindahl E, Hess B, and the GROMACS development team, GROMACS User Manual version 2019. http://www.gromacs.org
  • 39.Huang J, MacKerell AD., Jr Charmm36 all-atom additive protein force field: validation based on comparison to NMR data. J Comput Chem. 2013;34(25):2135–2145. doi: 10.1002/jcc.23354. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 40.Jorgensen WL, Chandrasekhar J, Madura JD. Comparison of simple potential functions for simulating liquid water. J Chem Phys. 1983;79(2):926–935. doi: 10.1063/1.445869. [DOI] [Google Scholar]
  • 41.Adcock SA, McCammon JA. Molecular dynamics: survey of methods for simulating the activity of proteins. Chem Rev. 2006;106(5):1589–1615. doi: 10.1021/cr040426m. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 42.Hess B, Bekker H, Berendsen HJC, et al. LINCS: a linear constraint solver for molecular simulations. J Comput Chem. 1997;18(12):1463–1472. doi: 10.1002/(SICI)1096-987X(199709)18:12<1463::AID-JCC4>3.0.CO;2-H. [DOI] [Google Scholar]
  • 43.Essmann U, Perera L, Berkowitz ML, et al. A smooth particle mesh Ewald method. J Chem Phys. 1995;103(19):8577–8593. doi: 10.1063/1.470117. [DOI] [Google Scholar]
  • 44.Humphrey W, Dalke A, Schulten K. VMD: visual molecular dynamics. J Mol Graph. 1996;14(1):33–38. doi: 10.1016/0263-7855(96)00018-5. [DOI] [PubMed] [Google Scholar]
  • 45.Vanommeslaeghe K, MacKerell AD., Jr Automation of the CHARMM general force field (CGenFF) I: bond perception and atom typing. J Chem Inf Model. 2012;52:12. doi: 10.1021/ci300363c. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 46.Frisch MJ, Trucks GW, Schlegel HB, et al., Gaussian 09, Revision A.02, Gaussian, Inc., Wallingford, CT, USA (2009)
  • 47.Cloete KJ, Šmit Z, Minnis-Ndimba R, Vavpetič P, du Plessis A, le Roux SG, Pelicon P. Physico-elemental analysis of roasted organic coffee beans from Ethiopia, Colombia, Honduras, and Mexico using X-ray micro-computed tomography and external beam particle induced X-ray emission. Food Chem X. 2019;2:100032. doi: 10.1016/j.fochx.2019.100032. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 48.Riyaz S, Parveen A, Azam A. Microstructural and optical properties of CuS nanoparticles prepared by sol—gel route. Perspect Sci. 2016;8:632–635. doi: 10.1016/j.pisc.2016.06.041. [DOI] [Google Scholar]
  • 49.Rashama C, Ijoma GN, Matambo TS. Elucidating biodegradation kinetics and biomethane potential trends in substrates containing high levels of phytochemicals: the case of avocado oil processing by-products. Waste Biomass Valoriz. 2022;13:2071–2081. doi: 10.1007/s12649-021-01663-z. [DOI] [Google Scholar]
  • 50.Greeshma KP, Thamizselvi R. Experimental and theoretical approach on green synthesized zinc oxide nanoparticles from combined leaf extracts of Catharanthus roseus and Morinda citrifolia for invitro anti-cancer studies. J Mol Liq. 2022;351:118636. doi: 10.1016/j.molliq.2022.118636. [DOI] [Google Scholar]
  • 51.Farhadi S, Siadatnasab F. Copper (I) sulfide (Cu2S) nanoparticles from Cu(II) diethyldithiocarbamate: synthesis, characterization and its application in ultrasound-assisted catalytic degradation of organic dye pollutants. Mater Res Bull. 2016;83:345–353. doi: 10.1016/j.materresbull.2016.06.030. [DOI] [Google Scholar]
  • 52.Basak M, Rahman L, Ahmed F, Biswas B, Sharmin N. The use of X-ray diffraction peak profile analysis to determine the structural parameters of cobalt ferrite nanoparticles using Debye-Scherrer, Williamson-Hall, Halder-Wagner and Size-strain plot: different precipitating agent approach. J Alloys Compd. 2022;895:162694. doi: 10.1016/j.jallcom.2021.162694. [DOI] [Google Scholar]
  • 53.Burton AW, Ong K, Rea T, Chan IY. On the estimation of average crystallite size of zeolites from the Scherrer equation: a critical evaluation of its application to zeolites with one-dimensional pore systems. Microporous Mesoporous Mater. 2009;117:75–90. doi: 10.1016/j.micromeso.2008.06.010. [DOI] [Google Scholar]
  • 54.Lau E, Carvalho L, Pereira A, Montanha G, Corrêa C, de Carvalho P, Hudson W, Ganin A, Fraceto L, Yiu H. Localization of coated iron oxide (Fe3O4) nanoparticles on tomato seeds and their effects on growth. ACS Appl Biomater. 2020 doi: 10.1021/acsabm.0c00216. [DOI] [PubMed] [Google Scholar]
  • 55.Moraghan JT, Grafton K. Distribution of selected elements between the seed coat and embryo of two black bean cultivars. J Plant Nutr. 2002;25(1):169–176. doi: 10.1081/PLN-100108788. [DOI] [Google Scholar]
  • 56.Janpengphat P, Senthong C, Meechoui S, Ingram K. Calcium in shell, seed coat, and seed in relation to resistance of peanut genotypes to Aspergillus flavus infection. Chiang Mai J Sci. 2014;41:531–541. [Google Scholar]
  • 57.Sharma SS, Karl-Josef D. The significance of amino acids and amino acid-derived molecules in plant responses and adaptation to heavy metal stress. J Exp Bot. 2006;57(4):711–726. doi: 10.1093/jxb/erj073. [DOI] [PubMed] [Google Scholar]
  • 58.Chongpraditnun P, Suzuki K, Kawaharada U, et al. Immunohistochemical localization of metallothionein in plant tissues. Water Air Soil Pollut. 1991;57:545–553. doi: 10.1007/BF00282918. [DOI] [Google Scholar]
  • 59.Pang Y, Applegate T. Effects of copper source and concentration on in vitro phytate phosphorus hydrolysis by phytase. J Agricult Food Chem. 2006;54:1792–1796. doi: 10.1021/jf052053b. [DOI] [PubMed] [Google Scholar]
  • 60.Lemtiri-Chlieh F, MacRobbie EA, Brearley CA. Inositol hexakisphosphate is a physiological signal regulating the K+-inward rectifying conductance in guard cells. Proc Natl Acad Sci U S A. 2000;97(15):8687–8692. doi: 10.1073/pnas.140217497. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 61.Shelar A, Nile SH, Singh AV, et al. Recent advances in nano-enabled seed treatment strategies for sustainable agriculture: challenges, risk assessment, and future perspectives. Nano-Micro Lett. 2023;15:54. doi: 10.1007/s40820-023-01025-5. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 62.Rohr LA, França-Silva F, Corrêa CG, Carvalho HWP, Gomes-Junior FG. Gomes-Junior FG. Soybean seeds treated with zinc evaluated by X-ray micro-fluorescence spectroscopy. Sci Agric. 2023;80:e20210131. doi: 10.1590/1678-992X-2021-0131. [DOI] [Google Scholar]
  • 63.Garnczarska M, Zalewski T, Kempka M. Water uptake and distribution in germinating lupine seeds studied by magnetic resonance imaging and NMR spectroscopy. Physiol Plant. 2007;130:23–32. doi: 10.1111/j.1399-3054.2007.00883.x. [DOI] [Google Scholar]
  • 64.Pereira A, Oliveira H, Fraceto L, Santaella C. Nanotechnology potential in seed priming for sustainable agriculture. Nanomaterials. 2021;11:267. doi: 10.3390/nano11020267. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 65.Rico C, Majumdar S, Duarte-Gardea M, Peralta-videa J, Gardea-Torresdey J. Interaction of nanoparticles with edible plants and their possible implications in the food chain. J Agricult Food Chem. 2011;59:3485–3498. doi: 10.1021/jf104517j. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 66.Wu H, Li Z. Nano-enabled agriculture: how do nanoparticles cross barriers in plants? Plant Commun. 2022;3(6):100346. doi: 10.1016/j.xplc.2022.100346. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 67.Szőllősi R, Molnár Á, Kondak S, Kolbert Z. Dual effect of nanomaterials on germination and seedling growth: stimulation vs. Phytotoxicity Plants. 2020;9:1745. doi: 10.3390/plants9121745. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 68.García-Ovando AE, Piña JER, Naranjo EUE, Chávez JAC, Esquivel K. Biosynthesized nanoparticles, and implications by their use in crops: effects over physiology, action mechanisms, plant stress responses and toxicity. Plant Stress. 2022;6:100109. doi: 10.1016/j.stress.2022.100109. [DOI] [Google Scholar]
  • 69.Nile SH, Thiruvengadam M, Wang Y, et al. Nano-priming as emerging seed priming technology for sustainable agriculture—recent developments and future perspectives. J Nanobiotechnol. 2022;20:254. doi: 10.1186/s12951-022-01423-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 70.Tovar GI, Briceño S, Suarez J, Flores S, González G. Biogenic synthesis of iron oxide nanoparticles using Moringa oleifera and chitosan and its evaluation on corn germination. Environ Nanotechnol Monit Manag. 2020;14:100350. [Google Scholar]
  • 71.Savassa S, Castillo-Michel H, Del Real P, Elena A, Reyes-Herrera J, Marques JP, de Carvalho PHW. Ag nanoparticles enhancing Phaseolus vulgaris seedling development: understanding nanoparticles migration and chemical transformation across seed coat. Environ Sci Nano. 2021 doi: 10.1039/D0EN00959H. [DOI] [Google Scholar]
  • 72.Mittal D, Kaur G, Singh P, Yadav K, Ali S. Nanoparticle-based sustainable agriculture and food science: recent advances and future outlook. Front Nanotechnol. 2020 doi: 10.3389/fnano.2020.579954. [DOI] [Google Scholar]
  • 73.Spielman-Sun E, Lombi E, Donner E, Avellan A, Etschmann B, Howard D, Lowry G. Temporal evolution of copper distribution and speciation in roots of Triticum aestivum exposed to CuO, Cu(OH)2, and CuS nanoparticles. Environ Sci Technol. 2018;52:9777–9784. doi: 10.1021/acs.est.8b02111. [DOI] [PubMed] [Google Scholar]
  • 74.Chen XG, Wu YH, Li NQ, et al. What role does the seed coat play during symbiotic seed germination in orchids: an experimental approach with Dendrobium officinale. BMC Plant Biol. 2022;22:375. doi: 10.1186/s12870-022-03760-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 75.Shang H, Ma C, Li C, Zhao J, Elmer W, White JC, Xing B. Copper oxide nanoparticle-embedded hydrogels enhance nutrient supply and growth of lettuce (Lactuca sativa) infected with Fusarium oxysporum f. sp. Lactucae. Environ Sci Technol. 2021;55(20):13432–13442. doi: 10.1021/acs.est.1c00777. [DOI] [PubMed] [Google Scholar]
  • 76.Radchuk V, Borisjuk L. Physical, metabolic and developmental functions of the seed coat. Front Plant Sci. 2014;5:510. doi: 10.3389/fpls.2014.00510. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 77.Zhang P, Georgiou CA, Brusic V. Elemental metabolomics. Briefings Bioinform. 2018;19(3):524–536. doi: 10.1093/bib/bbw131. [DOI] [PubMed] [Google Scholar]
  • 78.Hou Q, Bourgeas R, Pucci F, et al. Computational analysis of the amino acid interactions that promote or decrease protein solubility. Sci Rep. 2018;8:14661. doi: 10.1038/s41598-018-32988-w. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 79.Amir R, Galili G, Cohen H. The metabolic roles of free amino acids during seed development. Plant Sci. 2018;275:11–18. doi: 10.1016/j.plantsci.2018.06.011. [DOI] [PubMed] [Google Scholar]
  • 80.Del Moral LF, Rharrabti Y, Martos V, Royo C. Environmentally induced changes in amino acid composition in the grain of durum wheat grown under different water and temperature regimes in a Mediterranean environment. J Agric Food Chem. 2007;55(20):8144–8151. doi: 10.1021/jf063094q. [DOI] [PubMed] [Google Scholar]
  • 81.Wang Y, Jiang F, Ma C, Yi Ru, Tsang DCW, Xing B. Effect of metal oxide nanoparticles on amino acids in wheat grains (Triticum aestivum) in a life cycle study. J Environ Manag. 2019;241:319–327. doi: 10.1016/j.jenvman.2019.04.041. [DOI] [PubMed] [Google Scholar]
  • 82.Angelovici R, Fait A, Fernie AR, Galili G. A seed high-lysine trait is negatively associated with the TCA cycle and slows down Arabidopsis seed germination. New Phytol. 2011;189(1):148–159. doi: 10.1111/j.1469-8137.2010.03478.x. [DOI] [PubMed] [Google Scholar]
  • 83.Feduraev P, Skrypnik L, Riabova A, Pungin A, Tokupova E, Maslennikov P, Chupakhina G. Phenylalanine and tyrosine as exogenous precursors of wheat (Triticum aestivum L.) secondary metabolism through PAL-associated pathways. Plants. 2020;9:476. doi: 10.3390/plants9040476. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 84.Fraser CM, Chapple C. The phenylpropanoid pathway in arabidopsis. Arabidopsis Book. 2011;9:e0152. doi: 10.1199/tab.0152. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 85.Alfosea-Simón M, Simón-Grao S, Zavala-Gonzalez EA, Cámara-Zapata JM, Simón I, Martínez-Nicolás JJ, Lidón V, García-Sánchez F. Physiological, nutritional and metabolomic responses of tomato plants after the foliar application of amino acids aspartic acid, glutamic acid and alanine. Front Plant Sci. 2011;11:581234. doi: 10.3389/fpls.2020.581234. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 86.Olkhovych O, Volkogon M, Taran N, et al. The effect of copper and zinc nanoparticles on the growth parameters, contents of ascorbic acid, and qualitative composition of amino acids and acylcarnitines in Pistia stratiotes L. (Araceae) Nanoscale Res Lett. 2016;11:218. doi: 10.1186/s11671-016-1422-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 87.Yang HQ, Gao HJ, Zhi W, Sheng L, Yu F, Zi S, Wu X, Xue B. Physiological function of arginine and its metabolites in plants. Chinese. 2007;33(1):1–8. [PubMed] [Google Scholar]
  • 88.Schenck CA, Maeda HA. Tyrosine biosynthesis, metabolism, and catabolism in plants. Phytochemistry. 2018;149:82–102. doi: 10.1016/j.phytochem.2018.02.003. [DOI] [PubMed] [Google Scholar]
  • 89.Han M, Zhang C, Suglo P, Sun S, Wang M, Su T. l-Aspartate: an essential metabolite for plant growth and stress acclimation. Molecules. 2021;26(7):1887. doi: 10.3390/molecules26071887. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 90.Batista-Silva W, Heinemann B, Rugen N, Nunes-Nesi A, Araújo WL, Braun HP, et al. The role of amino acid metabolism during abiotic stress release. Plant Cell Environ. 2019;42:1630–1644. doi: 10.1111/pce.13518. [DOI] [PubMed] [Google Scholar]
  • 91.Jorgensena WL, Duffy EM. Prediction of drug solubility from structure. Adv Drug Deliv Rev. 2002;54:355–366. doi: 10.1016/S0169-409X(02)00008-X. [DOI] [PubMed] [Google Scholar]
  • 92.Delmondes P, Stefani R. Computational study of natural phenolic acid solubility, and their interactions with chitosan. MOL2NET. 2016 doi: 10.3390/mol2net-02-03862. [DOI] [Google Scholar]
  • 93.Calculator Plugins were used for structure and property prediction and calculation, Playground v1.5.0, (2023) ChemAxon (http://www.chemaxon.com).

Associated Data

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Data Availability Statement

The data supporting the findings reported is available upon reasonable request from the corresponding author.


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