Green Synthesis and Characterization of Silver Nanoparticles Using Myrsine africana Leaf Extract for Their Antibacterial, Antioxidant and Phytotoxic Activities

Nanotechnology is the study and control of materials at length scales between 1 and 100 nanometers (nm), where incredible phenomena enable new applications. It affects all aspects of human life and is the most active research topic in modern materials science. Among the various metallic nanoparticles used in biomedical applications, silver nanoparticles (AgNPs) are among the most important and interesting nanomaterials. The aim of this study was to synthesize AgNPs from the leaf extract of Myrsine africana to investigate their antibacterial, antioxidant, and phytotoxic activities. When the leaf extract was treated with AgNO3, the color of the reaction solution changed from light brown to dark brown, indicating the formation of AgNPs. The UV-visible spectrum showed an absorption peak at 438 nm, confirming the synthesis of AgNPs. Scanning electron microscopy (SEM) showed that the AgNPs were spherical and oval with an average size of 28.32 nm. Fourier transform infrared spectroscopy confirms the presence of bio-compound functional groups on the surface of the AgNPs. The crystalline nature of the AgNPs was confirmed by XRD pattern. These biosynthesized AgNPs showed pronounced antibacterial activity against Gram-positive and Gram-negative bacteria, with higher inhibitory activity against Escherichia coli. At 40 µg/mL AgNPs, the highest antioxidant activity was obtained, which was 57.7% and an IC50 value of 77.56 µg/mL. A significant positive effect was observed on all morphological parameters when AgNPs were applied to wheat seedlings under constant external conditions at the different concentrations. The present study provides a cost-effective and environmentally friendly method for the synthesis of AgNPs, which can be effectively used in the field of therapeutics, as antimicrobial and diagnostic agents, and as plant growth promoters.


Introduction
Recently, nanotechnology has attracted the attention of researchers due to its wide range of applications in the fields of medicine, agriculture, environment, and food [1]. This technology essentially focuses on the synthesis of tiny nanoparticles produced by chemical, physical, and biological processes, which contribute significantly to the control of plant and animal diseases and have shown considerable promise in improving the quality of human life and health conditions [2]. These nanoparticles range in size from 1 to 100 nm. However, the green synthesis of nanoparticles has become more important than chemical and physical distilled water and heated on a magnetic stirrer at 60 • C for 1 h. It was then filtered with Whatman No. 1 filter paper and the leaf filtrate was used for the synthesis of AgNPs [27].

Green Synthesis of AgNPs
To prepare the silver nitrate stock solution (1 mM), 80 mL of the plant leaf extract was mixed with 250 mL of the silver nitrate stock solution and incubated for 3 h at room temperature. After 3 h of incubation, a visual color change of the reaction solution was observed [27].

Characterization of Silver Nanoparticles 2.3.1. UV-Visible Spectroscopy
To determine the absorbance value of the nanoparticles in the range of 300-600 nm, a UV-Vis spectrophotometric study was performed [28]. The UV-Vis spectrophotometer was used to record the SPR of the biogenic AgNPs [29].

SEM-EDX
Scanning electron microscopy coupled with energy-dispersive X-rays (SEM-EDX) was used to analyze the morphology and composition of Ag-NPs [30]. A histogram of the size distribution of AgNPs was created using imageJ software.

XRD
The crystalline structure of the biosynthesized Ag-NPs was investigated by X-ray diffraction (XRD). The sample was analyzed between 3 and 90 theta values. Using Cu-Ka as the radiation source (=1.54), the XRD investigation was performed at a voltage and current of 40 KV and 30 mA, respectively [31].

FT-IR
The different functional groups responsible for the reduction and stabilization of the biosynthesized Ag-NPs were identified using FT-IR analysis (Cary 630 FTIR model, Tokyo, Japan). The KBr technique was used to perform the following FT-IR analysis: Under high pressure, 300 mg of biosynthesized Ag-NPs were thoroughly mixed with KBr to create a slice that was scanned at a wave number between 400 and 4000 cm −1 [32].
The agar well diffusion method was used to evaluate the bactericidal activity of Myrisine africana AgNPs. For the bacterial culture, nutrient broth media (Oxide: CM1) was utilized, and nutrient agar (Oxide: CMO337) was used for the bactericidal activity. The overnight culture was combined with freshly made nutrient agar medium and placed into sterile petri plates at 45 • C. For solidification, all petri dishes were placed in a laminar flow at room temperature. The striking of bacterial strains was performed in each plate then different concentrations (0.03, 0.05, 0.09, 0.11, and 0.13 mg/mL) of AgNPs was used and 100 uL of each concentration was put into respective well and was kept at 37 • C for 24 h. The diameter of the inhibition zone after 24 h was measured in millimeters (mm) to determine microbial growth. With the help of scale, the diameter of the clear zones around each well was measured [20,33].

Antioxidant Assay
The DPPH assay was used to determine the antioxidant potential of Ma-extract and Ma-AgNPs [20,34]. The stock solution was prepared by dissolving DPPH (12.5 mg) in 50 mL of methanol, and kept in the refrigerator. The plant sample solution was also prepared in methanol. The serial dilution of the solution was also prepared with different concentration (100, 50, 25, and 12.5 µg/mL). Further, 0.1 mL of each dilution was mixed with 3.0 mL of DPPH in a test tubes in kept them in to the incubator for half an hour at 37 • C. Ascorbic acid was used as standard. UV-Vis spectrophotometer was used to determine the absorbance against the standard at 517 nm. All the test tubes were repeated 3 times for the absorbance. The control sample was also prepared by using 2 mL of DPPH solution + 1 mL of methanol. The result Percentage inhibition was calculated by using given formula.

Percentage inhibition =
Absorbance o f test Absorsbance o f control × 100

Phytotoxicity Assesement of AgNPs
To study the phytotoxicity of AgNPs, morphological parameters of wheat cultivar Bakhtawar-38 were evaluated under the application of AgNPs. Healthy seeds collected from the National Agriculture Research Center (NARC) in Islamabad, Pakistan, were surface sterilized with 3% sodium hypochlorite for 5 min and then washed three times with distilled water. Seeds were then sown in sand under optimal conditions (65% humidity, +25 • C temperature, and an 8/16-h dark and light period). Eight-day-old wheat seedlings (two-leaf stage) were treated with AgNPs at concentrations of 10, 20, 40, and 80 mg/L. Plant roots were treated with nanoparticle solutions and the effects on morphology (plant fresh weight, root/shoot fresh weight, and root/shoot length) were recorded on the three consecutive days after treatment (i.e., day 9, 10, and 11). Root/shoot length was measured in cm using a measuring scale, while fresh weight was recorded in mg using an electric balance. The experiment was performed in triplicate.

Statistical Analysis
Data were statistically analyzed using Origin Pro version 9.1 software. All tests were performed in triplicate. Analysis of variance (ANOVA) was performed using the least significant differences (LSD) test to compare the significant differences (p ≤ 0.05) between groups.

Green Synthesis and Characterization of AgNPs
The plant extract and silver nitrate salt solution were mixed and incubated for 3 h. During this time, there was a visible color change in the reaction mixture. The apparent color of the solution changed from yellow-orange to dark brown, confirming the phytosynthesis of silver nanoparticles ( Figure 1). This color change was due to the surface plasmon resonance (SPR) activity of the NPs [35,36]. The amount of color is determined by the number of electrons that are released during the reduction of NO 3 to NO 2 , which reduces Ag + to metallic ions (Ag 0 ) [37]. Our work was supported by the findings of [38], which were identical to ours in terms of the visual change of the color of the solution.
The color change of the reaction solution was further investigated using the UV-Vis spectrum of the plant extract and AgNPs. The AgNPs showed an absorption peak at 438 nm caused by SPR due to the excitation of the free electrons of the metal during the formation of the AgNPs ( Figure 2). However, the plant extract did not show an absorption peak in this region. In general, these spectra provide information about the properties and formation of colloidal AgNPs. An absorption peak in the range of 400-500 nm is a characteristic feature of AgNPs [39]. number of electrons that are released during the reduction of NO3 to NO2, which reduces Ag + to metallic ions (Ag 0 ) [37]. Our work was supported by the findings of [38], which were identical to ours in terms of the visual change of the color of the solution. The color change of the reaction solution was further investigated using the UV-Vis spectrum of the plant extract and AgNPs. The AgNPs showed an absorption peak at 438 nm caused by SPR due to the excitation of the free electrons of the metal during the formation of the AgNPs ( Figure 2). However, the plant extract did not show an absorption peak in this region. In general, these spectra provide information about the properties and formation of colloidal AgNPs. An absorption peak in the range of 400-500 nm is a characteristic feature of AgNPs [39].   The color change of the reaction solution was further investigated using the UV-Vis spectrum of the plant extract and AgNPs. The AgNPs showed an absorption peak at 438 nm caused by SPR due to the excitation of the free electrons of the metal during the formation of the AgNPs ( Figure 2). However, the plant extract did not show an absorption peak in this region. In general, these spectra provide information about the properties and formation of colloidal AgNPs. An absorption peak in the range of 400-500 nm is a characteristic feature of AgNPs [39].  SEM is a powerful technique for evaluating surface structures, including nanoparticle size, morphology, and shape. A SEM image of these AgNPs shows their spherical and generally uniform shape ( Figure 3a). According to the particle size distribution histogram, the average size of AgNPs is 28.32 nm (Figure 3b). Previous studies also support our results [30].
Metallic silver ions were confirmed by energy dispersive X-ray detector. The EDX spectrum showed a strong absorption peak of the metallic silver ions in the range of 2.5-3.7 keV, while the silver nanocrystal showed absorption peaks in the range of 2.5-3.7 keV. Different types of elements in the form of peaks were detected together with silver ions. These elements were carbon and oxygen together with metallic silver (Figure 4). SEM is a powerful technique for evaluating surface structures, including nanoparticle size, morphology, and shape. A SEM image of these AgNPs shows their spherical and generally uniform shape (Figure 3a). According to the particle size distribution histogram, the average size of AgNPs is 28.32 nm (Figure 3b). Previous studies also support our results [30]. Metallic silver ions were confirmed by energy dispersive X-ray detector. The EDX spectrum showed a strong absorption peak of the metallic silver ions in the range of 2.5-3.7 keV, while the silver nanocrystal showed absorption peaks in the range of 2.5-3.7 keV. Different types of elements in the form of peaks were detected together with silver ions. These elements were carbon and oxygen together with metallic silver ( Figure 4). The XRD pattern of AgNPs showed peaks at 38.44, 44.50, 64.80, and 77.94° corresponding to 111, 200, 220, and 311 levels, respectively ( Figure 4). These diffraction patterns indicate the crystalline nature of the AgNPs [30]. Additional peaks at 30°, 54°, 56°, and 84° C were also observed, but these were due to biomolecules in the silver nanoparticles involved in the capping and reduction of AgNPs ( Figure 5). generally uniform shape (Figure 3a). According to the particle size distribution histogram, the average size of AgNPs is 28.32 nm (Figure 3b). Previous studies also support our results [30]. Metallic silver ions were confirmed by energy dispersive X-ray detector. The EDX spectrum showed a strong absorption peak of the metallic silver ions in the range of 2.5-3.7 keV, while the silver nanocrystal showed absorption peaks in the range of 2.5-3.7 keV. Different types of elements in the form of peaks were detected together with silver ions. These elements were carbon and oxygen together with metallic silver (Figure 4).  [30]. Additional peaks at 30°, 54°, 56°, and 84° C were also observed, but these were due to biomolecules in the silver nanoparticles involved in the capping and reduction of AgNPs ( Figure 5).  [30]. Additional peaks at 30 • , 54 • , 56 • , and 84 • C were also observed, but these were due to biomolecules in the silver nanoparticles involved in the capping and reduction of AgNPs ( Figure 5). FTIR spectroscopy is an essential technique for molecular figure printing, which can detect the functional group of plant secondary metabolites that act as capping or reducing agents [40]. Various bands appeared in the FTIR spectrum between 400 and 4000 Cm −1 . The bands at 1699, 1558, 1479, 1392, 1245, 1116, 1047, 723, 646, and 534 cm −1 correspond to C=C, C=O, C-C, C=C, -OH, C-N, and C-X stretching, respectively ( Figure 6). These functional groups indicate the presence of plant biocomponents as capping and stabilizing agents of AgNPs. These biomolecules are responsible for the reduction process of Ag+ to AgNPs [41]. FTIR spectroscopy is an essential technique for molecular figure printing, which can detect the functional group of plant secondary metabolites that act as capping or reducing agents [40]. Various bands appeared in the FTIR spectrum between 400 and 4000 cm − C=O, C-C, C=C, -OH, C-N, and C-X stretching, respectively ( Figure 6). These functional groups indicate the presence of plant biocomponents as capping and stabilizing agents of AgNPs. These biomolecules are responsible for the reduction process of Ag + to AgNPs [41]. FTIR spectroscopy is an essential technique for molecular figure printing, which can detect the functional group of plant secondary metabolites that act as capping or reducing agents [40]. Various bands appeared in the FTIR spectrum between 400 and 4000 Cm −1 . The bands at 1699, 1558, 1479, 1392, 1245, 1116, 1047, 723, 646, and 534 cm −1 correspond to C=C, C=O, C-C, C=C, -OH, C-N, and C-X stretching, respectively ( Figure 6). These functional groups indicate the presence of plant biocomponents as capping and stabilizing agents of AgNPs. These biomolecules are responsible for the reduction process of Ag+ to AgNPs [41].

Anti-Bacterial Activity
The antibacterial activity of Myrisine Africana AgNPs was evaluated by the agar well diffusion method. Different concentrations of plant based AgNPs were used. When we

Anti-Bacterial Activity
The antibacterial activity of Myrisine africana AgNPs was evaluated by the agar well diffusion method. Different concentrations of plant based AgNPs were used. When we increased the amount of ANPs, the growth of all bacterial strains was suppressed ( Figure 7). All strains showed the greatest inhibition at a dosage of 0.13 mg/mL. The highest antibacterial activity was observed against E. coli, a Gram-negative bacterium. It has already been described that even a very low concentration of AgNPs suppresses the growth of bacteria [42]. It is believed that the antibacterial effect of AgNPs is primarily due to the destruction of cell membranes. The antibacterial effect of AgNPs is inhibited by blocking intracellular signaling pathways [43]. In addition, studies revealed that the antibacterial mechanism of biogenic AgNPs is associated with cell membrane disruption, followed by the production of reactive oxygen species, which can alter normal functioning and cause DNA damage and protein denaturation [44]. Furthermore, Ag + ions generated by AgNPs disrupt the bacterial cell cycle, cause mitochondrial dysfunction, and induce apoptosis [45]. increased the amount of ANPs, the growth of all bacterial strains was suppressed ( Figure  7). All strains showed the greatest inhibition at a dosage of 0.13 mg/mL. The highest antibacterial activity was observed against E. coli, a Gram-negative bacterium. It has already been described that even a very low concentration of AgNPs suppresses the growth of bacteria [42]. It is believed that the antibacterial effect of AgNPs is primarily due to the destruction of cell membranes. The antibacterial effect of AgNPs is inhibited by blocking intracellular signaling pathways [43]. In addition, studies revealed that the antibacterial mechanism of biogenic AgNPs is associated with cell membrane disruption, followed by the production of reactive oxygen species, which can alter normal functioning and cause DNA damage and protein denaturation [44]. Furthermore, Ag + ions generated by AgNPs disrupt the bacterial cell cycle, cause mitochondrial dysfunction, and induce apoptosis [45].

Antioxidant Activity
When 2,2-diphenyl-1-picrylhydrazyl accepts an electron or a hydrogen radical, it transforms from a stable synthetic free radical to a stable molecule. Antioxidants convert the DPPH radical to the non-radical form in the DPPH test [46]. As a result, there is less absorption, and the DPPH solution turns yellow instead of purple. The different amounts of phytosynthesized AgNPs (10, 20, 30, 30, and 40 ug/mL) were used and compared with comparable concentrations of ascorbic acid as reference. At 40 ug/mL AgNPs, the highest antioxidant activity was obtained, which was 57.7%, while the standard (ascorbic acid)

Antioxidant Activity
When 2,2-diphenyl-1-picrylhydrazyl accepts an electron or a hydrogen radical, it transforms from a stable synthetic free radical to a stable molecule. Antioxidants convert the DPPH radical to the non-radical form in the DPPH test [46]. As a result, there is less absorption, and the DPPH solution turns yellow instead of purple. The different amounts of phytosynthesized AgNPs (10, 20, 30, 30, and 40 ug/mL) were used and compared with comparable concentrations of ascorbic acid as reference. At 40 ug/mL AgNPs, the highest antioxidant activity was obtained, which was 57.7%, while the standard (ascorbic acid) showed 67.29% at this concentration ( Figure 8). Similar results were reported in a previous study [47]. The study of antioxidant activity was conducted because free radicals are the main cause of most human diseases. In the human body, free radicals are the cause of many diseases. Antioxidant monitoring substances control the free radicals produced by our body. Numerous types of antioxidants that are harmful to human health are replaced by natural antioxidants [48]. Antioxidants help reduce oxidative stress in cells and are useful in a variety of human diseases, including inflammation, cardiovascular disease, and cancer [49]. More accessible, bioactive, and safe antioxidants from plants have been explored as an alternative to synthetic antioxidants [50]. AgNPs exhibit potent antioxidant activity by reducing oxidative stress in cells, which is beneficial for the treatment of many diseases such as cancer, lung infections, cardiovascular disease, and inflammatory infections. Previous researchers have studied, contrasted, and verified these findings [51].

Phytotoxicity of AgNPs
When AgNPs were applied to wheat seedlings, a significant positive effect was observed for all morphological parameters at the different concentrations under constant external conditions. Shoot length was significantly increased by AgNPs at a concentration of 10 mg/L on days 2 and 3 of treatment and at a concentration of 80 mg/L on days 1 and 3 of treatment. On the other hand, shoot length was increased by 20 mg/L AgNPs and decreased by 40 mg/L AgNPs on each of the first three days after treatment. However, there was no detectable difference between the effect and the control (Figure 9). The study of antioxidant activity was conducted because free radicals are the main cause of most human diseases. In the human body, free radicals are the cause of many diseases. Antioxidant monitoring substances control the free radicals produced by our body. Numerous types of antioxidants that are harmful to human health are replaced by natural antioxidants [48]. Antioxidants help reduce oxidative stress in cells and are useful in a variety of human diseases, including inflammation, cardiovascular disease, and cancer [49]. More accessible, bioactive, and safe antioxidants from plants have been explored as an alternative to synthetic antioxidants [50]. AgNPs exhibit potent antioxidant activity by reducing oxidative stress in cells, which is beneficial for the treatment of many diseases such as cancer, lung infections, cardiovascular disease, and inflammatory infections. Previous researchers have studied, contrasted, and verified these findings [51].

Phytotoxicity of AgNPs
When AgNPs were applied to wheat seedlings, a significant positive effect was observed for all morphological parameters at the different concentrations under constant external conditions. Shoot length was significantly increased by AgNPs at a concentration of 10 mg/L on days 2 and 3 of treatment and at a concentration of 80 mg/L on days 1 and 3 of treatment. On the other hand, shoot length was increased by 20 mg/L AgNPs and decreased by 40 mg/L AgNPs on each of the first three days after treatment. However, there was no detectable difference between the effect and the control (Figure 9).
For root length, a favorable effect was observed on 40 mg/L and 80 mg/L AgNPs compared to control plants on all three days after treatment. However, at an exposure level of 20 mg/L, root length initially increased on the first and second days before decreasing on the third day. In response to 10 mg/L AgNPs, root length was significantly increased on days one and three compared to control plants ( Figure 10).
The fresh weight of plants was also strongly affected by different concentrations of AgNPs. A significant decrease in seedling fresh weight was observed at the 10 mg/L and 40 mg/L exposure levels compared with the control on all three days after treatment. Control plants and plants treated with AgNPs at 20 mg/L showed a similar trend in fresh biomass. In contrast, only 80 mg/L AgNPs increased plant fresh weight on the second and third days after treatment compared to the other exposure levels and control plants ( Figure 11). For root length, a favorable effect was observed on 40 mg/L and 80 mg/L AgNPs compared to control plants on all three days after treatment. However, at an exposure level of 20 mg/L, root length initially increased on the first and second days before decreasing on the third day. In response to 10 mg/L AgNPs, root length was significantly increased on days one and three compared to control plants ( Figure 10). The fresh weight of plants was also strongly affected by different concentrations of AgNPs. A significant decrease in seedling fresh weight was observed at the 10 mg/L and 40 mg/L exposure levels compared with the control on all three days after treatment. Control plants and plants treated with AgNPs at 20 mg/L showed a similar trend in fresh biomass. In contrast, only 80 mg/L AgNPs increased plant fresh weight on the second and For root length, a favorable effect was observed on 40 mg/L and 80 mg/L AgNPs compared to control plants on all three days after treatment. However, at an exposure level of 20 mg/L, root length initially increased on the first and second days before decreasing on the third day. In response to 10 mg/L AgNPs, root length was significantly increased on days one and three compared to control plants ( Figure 10). The fresh weight of plants was also strongly affected by different concentrations of AgNPs. A significant decrease in seedling fresh weight was observed at the 10 mg/L and 40 mg/L exposure levels compared with the control on all three days after treatment. Control plants and plants treated with AgNPs at 20 mg/L showed a similar trend in fresh biomass. In contrast, only 80 mg/L AgNPs increased plant fresh weight on the second and   Shoot fresh weight was significantly decreased in response to concentrations of 10 mg/L and 40 mg/L AgNPs on all three days after treatment. The highest increases and decreases in shoot weight were recorded on the first and third days of plants treated with 10 mg/L AgNPs compared with all other treatments and control plants. In contrast, at a concentration of 20 mg/L AgNPs, shoot fresh weight increased continuously on all three days after treatment. In the plants treated with 80 mg/L AgNPs, shoot weight was also increased on the second and third days ( Figure 12).
Different concentrations of AgNPs also showed a significant effect on the fresh weight of roots of eight-day-old wheat seedlings. On the first day, root fresh weight was significantly lower in plants treated with 80 mg/L AgNPs compared to all other treatments on the first day and to the control. On the second day, root weight decreased only in plants treated with 40 mg/L, while it increased in plants treated with 10, 20, and 80 mg/L compared to untreated plants. On the third day, the highest root weight was recorded in the plants treated with 20 mg/L AgNPs compared to the third day of all other treatments and control plants ( Figure 13). Shoot fresh weight was significantly decreased in response to concentrations of 10 mg/L and 40 mg/L AgNPs on all three days after treatment. The highest increases and decreases in shoot weight were recorded on the first and third days of plants treated with 10 mg/L AgNPs compared with all other treatments and control plants. In contrast, at a concentration of 20 mg/L AgNPs, shoot fresh weight increased continuously on all three days after treatment. In the plants treated with 80 mg/L AgNPs, shoot weight was also increased on the second and third days ( Figure 12). Different concentrations of AgNPs also showed a significant effect on the fresh weight of roots of eight-day-old wheat seedlings. On the first day, root fresh weight was significantly lower in plants treated with 80 mg/L AgNPs compared to all other treatments on the first day and to the control. On the second day, root weight decreased only in plants  Previous studies also reported that AgNPs had a positive effect on plant morphology, including increased fresh weight and longer roots and shoots [20,52]. In our study, the most significant effects were observed on root weight, with all four concentrations showing significant differences compared to the control. Moreover, root weight gradually de- Previous studies also reported that AgNPs had a positive effect on plant morphology, including increased fresh weight and longer roots and shoots [20,52]. In our study, the most significant effects were observed on root weight, with all four concentrations showing significant differences compared to the control. Moreover, root weight gradually decreased with increasing concentration on the third day after treatment, suggesting that these effects were dose-dependent. Similar results were obtained by Mirzajani et al. (2013), who found that root growth of Orzya sativa L. increased up to 30 g/mL but decreased at 60 g/mL [53]. In our study, a concentration of 10 mg/L AgNPs was found to be non-toxic for all parameters. This finding suggests that lower concentration of AgNPs could be beneficial for plant growth by improving plant growth parameters [54]. Similar results were reported by Mustafa et al., (2020), who found that 10 mg/L AgNPs increased soybean root growth, while 50 mg/L decreased root length and weight [55]. Hasan et al. also reported the same results on lettuce [56]. Our results indicate that 80 mg/L AgNPs at higher concentrations decreased morphological parameters compared with the control, but the effects gradually increased after three days in all treatments. Thus, it appears that the beneficial effects of higher doses are timedependent. These results are consistent with those of Mustafa et al., (2015, 2016) on soybean, who found that AgNPs at a concentration of 80 mg/L initially increased seedling weight and root length before decreasing under flood conditions [56,57]. Higher concentrations of AgNPs (50 mg/L) also increased hypocotyl weight in a time-dependent manner [55]. This suggests that the phytotoxicity of AgNPs is dose-dependent, while higher concentrations may be time-dependent for their beneficial effects.

Conclusions
In this study, a sustainable, green approach was adopted for efficient synthesis using the leaf extract of M. africana., which yielded spherical shaped AgNPs with an average size of 28.32 nm. Myrisins africana-AgNPs showed significant bactericidal activity with a higher zone of inhibition against E. coli. They also showed remarkable antioxidant activity in the form of DPPH radical scavenger. Under the different concentrations and constant external conditions, a noticeable positive effect was observed on all morphological parameters of wheat seedlings. The results of the present study suggest that AgNPs can be used as antibiotics, antioxidants, and phytotoxic agents in the future as they are non-toxic, inexpensive, and highly effective.