Productivity and Phytochemicals of Asclepias curassavica in Response to Compost and Silver Nanoparticles Application: HPLC Analysis and Antibacterial Activity of Extracts

The application of compost and metallic nanoparticles has a significant impact on the productivity and chemical composition of horticulture plants. In two subsequent growing seasons, 2020 and 2021, the productivity of Asclepias curassavica L. plants treated with various concentrations of silver nanoparticles (AgNPs) and compost was assessed. In the pot experiments, the soil was amended with 25% or 50% compost, and the plants were sprayed with 10, 20, and 30 mg/L of AgNPs. Scanning electron microscopy (SEM), transmission electron microscopy (TEM), X-ray diffraction analysis (XRD), and dynamic light scattering (DLS) were used to characterize AgNPs. The TEM measurements of AgNPs showed that the particles had spherical forms and ranged in size from roughly 5 to 16 nm. Leaf methanol extracts (LMEs) were prepared from the treated plants and assayed against the growth of two soft rot bacteria, Dickeya solani and Pectobacterium atrosepticum. The maximum plant height, diameter, number of branches/plant, total fresh weight (g), total dry weight (g), and leaf area (cm2) was recorded when levels of 25% compost + AgNPs 20 mg/L, 25% compost, or 50% + AgNPs 20 mg/L, 25% compost + AgNPs 30 mg/L or 50% compost + AgNPs 20 mg/L, 50% compost + AgNPs 20 mg/L, 50% compost + AgNPs 30 or 20 mg/L, and 25% compost + AgNPs 30 mg/L, respectively, were applied. The plants treated with 25% or 50% compost + 30 mg/L AgNPs showed a high chlorophyll content, while the plants treated with 50% compost + AgNPs 30 mg/L or 20 mg/L showed the highest extract percentages. The highest inhibition zones (IZs), 2.43 and 2.2 cm, against the growth of D. solani were observed in the LMEs (4000 mg/L) extracted from the plants treated with compost (v/v) + AgNPs (mg/L) at the levels of 50% + 30 and 25% + 30, respectively. The highest IZs, 2.76 and 2.73 cm, against the growth of P. atrosepticum were observed in the LMEs (4000 mg/L) extracted from the plants treated at the levels of 50% + 30 and 25% + 30, respectively. Several phenolic compounds such as syringic acid, p-coumaric acid, chlorogenic acid, cinnamic acid, ellagic acid, caffeic acid, benzoic acid, gallic acid, ferulic acid, salicylic acid, pyrogallol, and catechol, as well as flavonoid compounds such as 7-hydroxyflavone, naringin, rutin, apigenin, quercetin, kaempferol, luteolin, hesperidin, catechin, and chrysoeriol, were identified in the LMEs as analyzed by HPLC with different concentrations according to the treatment of compost + AgNPs used for the plants. In conclusion, the specific criteria that were utilized to measure the growth of A. curassavica revealed the novelty of compost and AgNPs combination treatments, particularly at a concentration of 50% compost + AgNPs 30 mg/L or 20 mg/L, which is better for the growth and phytochemical production of A. curassavica in the field.

To the best of our knowledge, the Asclepias curassavica plant has not received much attention from researchers despite the fact that it has a variety of purposes in both ornamental gardening and medical bioactivity. AgNPs and compost are being applied to this plant for the first time.
Therefore, the aim of this experiment was to investigate the effect of compost and silver nanoparticles at various concentrations on Asclepias curassavica growth, and the phytochemical as well as biological activity of these substances against Dickeya solani and Pectobacterium atrosepticum, two bacteria that cause soft rot.

UV-Vis and X-ray Diffraction (XRD) Analyses
The UV-Vis absorption spectra of the produced AgNPs were examined between 200 and 1000 nm ( Figure 1A). The majority of AgNPs contain a surface plasmon resonance (SPR) band between 420 and 550 nm [41][42][43], which is caused by the excitation of free electrons. AgNPs were found to have an SPR value of 446 nm, which is consistent with results from several other studies [44][45][46]. The crystal structure and phase of nanoparticles, including AgNPs, are typically examined using XRD [47]. Figure 1B shows the XRD pattern of the synthesized AgNPs. The The crystal structure and phase of nanoparticles, including AgNPs, are typically examined using XRD [47]. Figure 1B shows the XRD pattern of the synthesized AgNPs. The primary peaks, which correspond to the 111, 200, 220, and 311 planes, are located at (2θ) 37.51 • , 42.81 • , 66.44 • , and 79.29 • , respectively. These peaks confirm the formation of AgNPs.
The results are in agreement and demonstrate that most AgNPs have a face-centered cubic material (fcc) structure and are consistent with JCPDS card number 89 3722 [48]. The XRD properties are detailed in Table 1. Information collected from XRD measurements, including the prominent peak, the d-spacing, and the predicted 2θ value for AgNPs, are presented in Table 2. The findings, taken as a whole, provide evidence that the naturally occurring structure of the synthesized AgNPs is crystalline.

Particle Size Distribution and Morphological Characterization of the Synthesized AgNPs
A common technique for determining how the sizes of particles are dispersed in a colloidal fluid is dynamic light scattering (DLS) [49]. The DLS analysis in the current study revealed that the particle size distribution of the biosynthesized AgNPs in the aqueous medium was broad; however, there was a single peak distribution corresponding to the average particle size, which was found to be 57.3 nm at 11.1 • (Figure 2). AgNPs had an average diameter of 87.6 nm at 90.0 • . XRD properties are detailed in Table 1. Information collected from XRD measurements,  including the prominent peak, the d-spacing, and the predicted 2θ value for AgNPs, are  presented in Table 2. The findings, taken as a whole, provide evidence that the naturally occurring structure of the synthesized AgNPs is crystalline.

Particle Size Distribution and Morphological Characterization of the Synthesized AgNPs
A common technique for determining how the sizes of particles are dispersed in a colloidal fluid is dynamic light sca ering (DLS) [49]. The DLS analysis in the current study revealed that the particle size distribution of the biosynthesized AgNPs in the aqueous medium was broad; however, there was a single peak distribution corresponding to the average particle size, which was found to be 57.3 nm at 11.1° ( Figure 2). AgNPs had an average diameter of 87.6 nm at 90.0°. One of the most effective methods for determining the appearance of the surface is scanning electron microscopy (SEM), which allows us to directly observe the nanoparticles [50]. The SEM investigation revealed that the powders with a lower degree of miscibility are composed of spherical-appearing pure AgNPs ( Figure 3A). The SEM images One of the most effective methods for determining the appearance of the surface is scanning electron microscopy (SEM), which allows us to directly observe the nanoparticles [50]. The SEM investigation revealed that the powders with a lower degree of miscibility are composed of spherical-appearing pure AgNPs ( Figure 3A). The SEM images demonstrated how the AgNPs combined to form lager particles. This effect could be explained by the existence of free static charges on the surface of the AgNPs [47,51].
According to the TEM findings, spherical AgNPs with a size range of roughly 5 to 16 nm were formed ( Figure 3B). The particle size distribution graph using TEM analysis is presented in Figure 3C. The majority of the AgNPs were found to be spread out, and only a few were found to be clumped together in groups of different sizes. The difference in size between the DLS and TEM methods is acceptable because, unlike in TEM [52,53], the diameter of the particles in DLS is determined with a layer of solvent in the scattered phase. demonstrated how the AgNPs combined to form lager particles. This effect could be explained by the existence of free static charges on the surface of the AgNPs [47,51]. According to the TEM findings, spherical AgNPs with a size range of roughly 5 to 16 nm were formed ( Figure 3B). The particle size distribution graph using TEM analysis is presented in Figure 3C. The majority of the AgNPs were found to be spread out, and only a few were found to be clumped together in groups of different sizes. The difference in size between the DLS and TEM methods is acceptable because, unlike in TEM [52,53], the diameter of the particles in DLS is determined with a layer of solvent in the sca ered phase.

FTIR Analysis
As illustrated in Figure 4, the FTIR spectrum reveals numerous functional groups in various locations. The peaks in the 3443 cm −1 and 2924 cm −1 were a ributed to the aldehyde-C-H-and O-H-stretching of alcohol compounds [54,55]. The existence of C=O groups (aldehydes and ketones) in the produced AgNPs was confirmed by the peak at 2362 cm −1 [40]. Furthermore, the peak found at 1633 cm −1 demonstrated the carbonyl group's (C=O) stretching vibration and the amine group's N-H bending [55]. The spectral bands observed at the 1107 and 1049 wavenumbers were assigned to the stretching vibrations of the C-O bond, as reported in previous studies [56,57]. Furthermore, it is plausible that the peak observed at 595 cm −1 may be a ributed to the stretching of C-N bonds in amine functional groups, as suggested by previous research [58]. This investigation demonstrates the contradictory behavior of molecules that may be involved in the stabilization and reduction of silver nanoparticles [59].

FTIR Analysis
As illustrated in Figure 4, the FTIR spectrum reveals numerous functional groups in various locations. The peaks in the 3443 cm −1 and 2924 cm −1 were attributed to the aldehyde-C-H-and O-H-stretching of alcohol compounds [54,55]. The existence of C=O groups (aldehydes and ketones) in the produced AgNPs was confirmed by the peak at 2362 cm −1 [40]. Furthermore, the peak found at 1633 cm −1 demonstrated the carbonyl group's (C=O) stretching vibration and the amine group's N-H bending [55]. The spectral bands observed at the 1107 and 1049 wavenumbers were assigned to the stretching vibrations of the C-O bond, as reported in previous studies [56,57]. Furthermore, it is plausible that the peak observed at 595 cm −1 may be attributed to the stretching of C-N bonds in amine functional groups, as suggested by previous research [58]. This investigation demonstrates the contradictory behavior of molecules that may be involved in the stabilization and reduction of silver nanoparticles [59].

Effect of Compost and AgNPs on Vegetative Growth of A. curassavica
According to the findings in Table 3, compost and AgNPs have a positive impact on the vegetative parameters of A. curassavica plants including plant height (cm), plant diameter (cm), branch number/plant, leaf fresh weight (g), leaf dry weight (g), and leaf area (cm 2 ), which gradually increased as the concentration increased in comparison to untreated plants. In contrast, the higher plant height was obtained by treating plants with 50% compost + AgNPs 20 mg/L (58.05 cm) in the first season and 25% compost + AgNPs 20 mg/L in the second season (61.66 cm), while the lower plant height was obtained by

Effect of Compost and AgNPs on Vegetative Growth of A. curassavica
According to the findings in Table 3, compost and AgNPs have a positive impact on the vegetative parameters of A. curassavica plants including plant height (cm), plant diameter (cm), branch number/plant, leaf fresh weight (g), leaf dry weight (g), and leaf area (cm 2 ), which gradually increased as the concentration increased in comparison to untreated plants. In contrast, the higher plant height was obtained by treating plants with 50% compost + AgNPs 20 mg/L (58.05 cm) in the first season and 25% compost + AgNPs 20 mg/L in the second season (61.66 cm), while the lower plant height was obtained by treating plants with 0% compost + 10 mg/L AgNPs in both seasons (36.61 and 41.89 cm, respectively). In the first and second seasons, respectively, the application of the 50% compost + AgNPs 20 and 50% compost +30 mg/L treatments revealed the highest diameter values of A. curassavica plants with 43.69 cm and 45 cm, respectively. Values are means ± 2SD. The means with the same letter/s within the same column have no significant difference according to LSD0.05. ns: Not significant.
The plants that were treated with 25% compost + AgNPs 30 mg/L in the first season and 50% compost + AgNPs 20 mg/L in the second season produced the highest number of branches/plant. The highest total fresh weight (g) was produced by the application of 50% compost + AgNPs 20 mg/L (62.73 g) followed by 50% compost + AgNPs 10 mg/L (59.97 g) in the first season, and 50% compost + AgNPs 30 mg/L (63.67 g) followed by 50% compost + AgNPs 20 mg/L (62.81 g) in the second season.
In both seasons, 50% compost + AgNPs 30 or 20 mg/L produced the greatest results for the total dry weight (g). In the first season, this result was 19.51 and 19.43 g, respectively, but in the second season, it was 24.10 and 22.91 g. Additionally, 25% compost + AgNPs 30 mg/L (16.2 and 16.2 cm 2 ) had the greatest impact on leaf area (cm 2 ) compared to the control (7.26 and 8.45 cm 2 ) for both seasons. Table 4 show that the compost and AgNPs significantly affected the chemical components of A. curassavica plants, including chlorophyll content (measured in SPAD units) and leaf methanol extract (LME%) ( Table 4). The plants treated with 25% or 50% compost + 30 mg/L AgNPs had the best results for chlorophyll content, with values of 62.64 and 62.44 SPAD unit, respectively; however, there was no significant difference in the second season. The treated plants with 50% compost + AgNPs 20 mg/L for the first season and 50% compost + AgNPs 30 mg/L for the second season had the greatest percentages of LMEs (8.31% for the first season and 8.34% for the second season).

Antibacterial Activity of A. curassavica Methanolic Leaf Extracts
The leaf methanolic extracts (LMEs) from A. curassavica plants treated with various levels of compost (v/v) + AgNPs (mg/L) are listed in Table 5 for their antibacterial activities. All of the LME concentrations utilized had a noticeable impact on the growth of Dickeya solani and Pectobacterium atrosepticum. By gradually raising the LME concentration, the inhibition zones (IZs cm) against the development of both bacteria were raised.  The LMEs at the concentrations of 4000, 4000, 4000, and 2000 mg/L, respectively, from the plants treated with compost (v/v) + AgNPs (mg/L) at the levels of 50% + 30, 25% + 30, 50% + 20, and 50% + 30, respectively, were found to have the highest IZs of 2.43, 2.2, 2.13, and 2.03 cm, reported against the growth of D. solani.
Additionally, the impact of the LMEs was significantly affected by the treatments of A. curassavica plants with compost + AgNPs at various doses because bacterial growth was inhibited. Plants treated with 25% or 50% compost + AgNPs 30 mg/L showed the greatest antibacterial activity of LMEs.
The determined minimum inhibitory concentrations (MICs) of the LMEs (Table 6)   Gentamicin 20 mg/disc 30 35 The LME of plants treated with amounts of compost (v/v) + AgNPs (mg/L) of 25% + 30 and 50% + 30 had the best MIC value against P. atrosepticum growth, which was 30 mg/L. The most effective concentration of LME on the growth of bacteria was obtained by treating plants with 25% or 50% compost + AgNPs 30 mg/L.
The four PCs with the highest concentrations were ferulic acid (16.74 g/g), syringic acid (12.31 g/g), pyrogallol (11.87 g/g), and p-coumaric acid (9.14 g/g) in the LME of plants treated with 50% compost + 10 mg/L AgNPs. The most prevalent PC in LME from the plants treated with 0% compost + 20 mg/L AgNPs was p-coumaric acid (11.42 g/g). Salicylic acid (11.98 g/g) and catechol (8.36 g/g) were present in the LME of the plants treated with 50% compost + 30 mg/L AgNPs as the major PCs.
The four PCs with the highest concentrations were ferulic acid (16.74 g/g), syringic acid (12.31 g/g), pyrogallol (11.87 g/g), and p-coumaric acid (9.14 g/g) in the LME of plants treated with 50% compost + 10 mg/L AgNPs. The most prevalent PC in LME from the plants treated with 0% compost + 20 mg/L AgNPs was p-coumaric acid (11.42 g/g). Salicylic acid (11.98 g/g) and catechol (8.36 g/g) were present in the LME of the plants treated with 50% compost + 30 mg/L AgNPs as the major PCs.

Discussion
The Asclepias curassavica L. plants (Asclepiadaceae family) or Apocynaceae family were treated with compost and silver nanoparticles (AgNPs), and the results indicated some positive effects on the vegetative growth parameters (plant height, plant diameter, number of branches/plant, leaf area, total fresh weight, total dry weight), total chlorophyll (SPAD unit), and the percentage of leaf methanol extracts (LMEs) in both successive seasons. The LMEs taken from the plants treated with the investigated treatments also contained a number of phenolic and flavonoid chemicals that were identified using HPLC analysis.
The results of the vegetative parameters and all of the photosynthetic pigment contents of fenugreek plants were enhanced by the foliar application of AgNPs concentrations of 20 and 40 mg/L [60]. The considerable promotion of photosynthesis by AgNPs, which was strongly associated with the alteration in nitrogen metabolism [61,62], was noteworthy. The action of AgNPs in suppressing ethylene signaling in the fenugreek plant may be the reason for the induced growth increases brought on by varied AgNPs concentrations [63]. The increased growth characteristics, photosynthetic pigments, and IAA of treated plants may be responsible for these increases in yield and chemical components [60].
Vinblastine from the Catharanthus roseus plant (Apocynaceae family) was isolated in high concentrations, which were visible in explants treated with 75 mg/L SNPs and 50 mg/L AgNPs [64]. Different doses of AgNPs had a an impact on the callus proliferation and increased the callus biomass of Caralluma tuberculata (family Apocynaceae); using AgNPs at 60 mg/L in combination with 0.5 mg/L2,4-D and 3.0 mg/L BA, the maximum fresh and dry biomass buildup of callus was noted [65]. The average number of leaves, number of branches, and carbohydrate content of the leaves of sunflower plants were all positively impacted by foliar spraying with 50 mL/L of AgNPs. There was no significant interaction among organic fertilizers, AgNPs, and salicylic acid on the vegetative parameters of sunflowers [66]. Different methods of applying AgNPs to the lotus (Nelumbo nucifera) increased plant height, leaf diameter, fresh leaf weight, dried leaf weight, and various biochemical characteristics compared to the control. The diameter and chlorophyll content of upright and floating leaves showed a positive correlation with dry leaf mass [67].
AgNPs improved plant qualitative and quantitative yield and increased plant yield and biochemical content of garden thyme (Thymus vulgaris L.) exposed to UV-B stress [68].
The growth of the Lilium cv. Mona Lisa was encouraged by soaking its bulbs in various concentrations of AgNPs, as shown by the increased accumulation of leaf and bulb biomass and the hastened flowering. The treated plants also produced more flowers and flowered for a longer period of time. The leaves gained the most chlorophyll a, chlorophyll b, and carotenoids with 100 ppm AgNPs [69]. All concentrations of applied colloidal AgNPs accelerated flowering, increased bulb diameter, and increased the fresh weight of the aboveground portion of the lily plants and bulbs [70]. The quality and quantity of cut flowers and bulbs produced by lily plants increased with the use of AgNPs solutions at various concentrations. All morphological traits rose on average by 26.29% with AgNPs compared to controls, with the exception of vase life [71]. The tulips that were exposed to 100 mg/L AgNPs flowered earlier and had longer stems for cut flowers, larger petals, and greater stem diameter [72].
One of the most commonly utilized nanomaterials is silver nanoparticles (AgNPs); however, studies on plants have shown that AgNPs are hazardous to them at the molecular, cellular, and physiological levels [7,73]. AgNPs are been released have the capacity to penetrate various media and finally reach plant rhizospheres [74,75]. Another result is that the AgNPs are inevitably absorbed by crops and readily enter the food chain [76], having an impact on both food production and food quality as well as posing a risk to human health [77]. When sprayed on rice plants at a concentration of 60 µg/mL, AgNPs not only infiltrated the cell wall but also disrupted the cell shape and structural components and inhibited root growth since AgNPs may only cause harm to plants when utilized in concentrations over a certain point [78]. Additionally, they cause root elongation in Arabidopsis thaliana [79] and both vegetative growth and root elongation in Lolium multiflorum [80]. AgNPs inhibit plant growth by impairing various stages of cell division and collapsing root cortical cells, epidermis, and root caps [80][81][82].
The absorbed AgNPs altered the structure of the thylakoid membrane due to the AgNPs' accumulation in leaves, which reduced the amount of chlorophyll and inhibited plant growth [79]. After being exposed to 50 mg/L of AgNPs, Vigna radiata seedlings' total chlorophyll content drastically decreased [83]. As a result of exposure to AgNPs, numerous plants were reported to have significantly less total chlorophyll content [84][85][86]. AgNPs also had an impact on the homeostasis of water and other small molecules within the plant body, as well as the balance between the oxidant and antioxidant systems [79].
Compost has been demonstrated to improve soil structure, increase permeability and infiltration, and increase soil organic matter and water-holding capacity [87,88]. If the compost was tilled into the soil, Asclepias tuberosa transplants benefited more frequently from the compost's better growth and reproduction. Compost had no benefit for the production of flower and seeds. It can be helpful in promoting better growth in prairie plots, but its use can have unfavorable effects in other conditions [89]. Another study revealed that the maximum plant growth of Acacia nilotica in pot trials was recorded when a 75% compost level was applied, while the minimum plant growth in the field trial was observed without any compost application. The increase in growth of A. nilotica plants was reported with the increases in the amount of compost mixture when a 100% compost level was applied, while the minimum was observed [90].
The combination of biochar-mineral complex and compost stimulated the microbial process in organic farming, leading to better production of vegetables by improving the soil properties [91]. Compost at the rate of 15 ton/feddan enhanced plant height, number of branches, total fresh or dry weight/plant and per feddan, chemical percentages, and chlorophyll a, b, and a + b of dragonhead (Dracocephalum moldavica) plants [92]. When the proportion of compost in the media increased, seedlings of Angelica arch-angelica, Marrubium vulgare, and Thymus vulgaris had higher shoot and root dry weights and mineral concentrations [93].
Under normal or saline-sodic soil conditions, the application of compost exhibited a positive impact on the growth parameters of plants [94]. Compost's high organic content boosts microbial activity in soils with high salinity, making more nutrients and minerals available to plants, which stimulates crop growth and yield [95][96][97][98].
In the present work, the growth of the two soft rot bacteria Dickeya solani and Pectobacterium atrosepticum was inhibited by the treatment of methanol leaf extracts from the collected plants with various treatments of compost and AgNPs in the current study. The antimicrobial activity of plant extract is due to the presence of secondary metabolites such as tannin, saponin, phenolics, flavonoids, and glycosides [99,100]. The growth of Bacillus subtilis, Staphylococcus aureus, Escherichia coli, and Klebsiella pneumoniae were all inhibited by the methanol extract of A. curassavica, but Proteus vulgaris was not [101]. The methanolic extracts of A. curassavica were observed to have antimicrobial activity against the growth of Bacillus subtilis, Staphylococcus aureus, Proteus vulgaris, Escherichia coli, and Klebsiella pneumoniae at various levels [102].
The Pinus halepensis cone extract's n-butanol fraction, with inhibition zones (IZs) of 14.33 mm and 12.33 mm, respectively, had the highest activity against D. solani and P. atrosepticum at a concentration of 2000 g/mL [103]. The oily extract from Bougainvillea spectabilis was found to be effective against the growth of D. solani at a concentration of 4000 g/mL, with an IZ value of 12.33 mm [104]. The growth of P. atrosepticum was significantly inhibited by an ethanol extract of Moringa oleifera seeds from ripened pods that contained the plant's primary polyphenolic components vanillic acid, benzoic acid, naringenin, chlorogenic acid, and myricetin [105]. Furthermore, phenolic and flavonoids from plant extracts have demonstrated significant antimicrobial properties. For example, ferulic acid showed antibacterial activity against D. solani, with an IZ ranging from 6.00 to 25.75 mm at various doses, but chlorogenic acid was ineffective [104].
Flavonoids, fixed oils, phenols, quinines, tannin, terpenoid, glycosides, coumarins, sugars, xanthoprotein, saponin, and steroids were present in the leaf, stem, and root extracts of A. curassavica [102,110,111]. Steroids, glycosides, phenols, and saponins were found in the methanol extracts of A. curassavica root and leaf, while flavonoids and resins were present in smaller amounts [102]. The total phenolics in A. muricata treated with various concentrations of AgNPs (250-1000 ppm) did not differ significantly. A. muricata leaves treated with AgNPs differed significantly from the control in terms of their flavonoid content [112].
To the best of our knowledge, this is the first study to examine how different compost and AgNPs combination treatments affect the productivity, growth, and phytochemicals of A. curassavica plants as measured over the course of two successive growing seasons. Although using synthesized nanoparticles as biostimulants has many intrinsic advantages, problems such as toxicity at high concentrations and dangerous disposal to the environment may limit their continuing usage, which opens new research opportunities.
A further limitation is that the stability of nanoparticles in the environment is another tough feature in utilizing them. The size of the particles and their affinity for other environmental components heavily influence the suspension's stability. The poorer stability of the metal nanoparticles in nature makes them more susceptible to oxidation in the air. These nanoparticles are kept in a specialized environment of inert gases because they cannot be kept in regular environmental conditions for use in the future [113,114].

Synthesis of Silver Nanoparticles (AgNPs)
Silver nanoparticles (AgNPs) were synthesized chemically using analytical-grade ethanol, silver nitrate (AgNO 3 ), and sodium borohydride (NaBH 4 ). In this procedure, sodium borohydride served as a reducing agent while ethanol served as a stabilizing agent. A homogeneous solution was created by dissolving 500 mg of AgNO 3 in 20 mL of ethanol and stirring it with a magnet stirrer for 1 h [54]. This step is necessary for the production of silver particles. After that, 500 mg of NaBH 4 was added to this solution, one drop at a time. When the solution changes from clear to black, this means that AgNPs are being produced. The precipitation was then collected, filtered, and repeatedly washed with ethanol and deionized water. The dried nanoparticles were maintained in a dark bottle for further characterization studies.

Characterization of AgNPs
The morphology, surface, and shape of the AgNPs were characterized by scanning electron microscopy (SEM) at 10 kV (JSM-6360 LA, JEOL, Tokyo, Japan) with a 3 mm working distance and transmission electron microscopy (TEM) using the JEM-2100 microscope (JEOL, Tokyo, Japan). The presence of the produced AgNPs was investigated using a UV-visible spectrophotometer (Shimadzu, Tokyo, Japan), with the reduction of pure Ag+ ions verified via measurement at UV-245 double-beam (200-1000 nm). The X-ray diffraction analysis (XRD) patterns were registered in a diffractometer (Shimadzu XRD-6100) using CuKα radiation (k = 1:5406 A • ) operated at a voltage of 40 kV and a current of 30 mA. Data were collected over a 2θ range of 5-80 • , 0.0200 steps, and 10 s of counting time per step. Based on the XRD peak widths, the crystallite domain size was determined. They must be free of non-uniform moieties, according to the assumption. With the help of the Debye-Scherrer equation, the average size of the AgNPs may be determined. A particle size analyzer (PSA, MALVERN, ZETASIZER Ver.6.20) was used to examine particle size distribution. Quartz was used to examine the material, Thetes, the temperature was set at 25 • C, and pure water was utilized for viscosity and refractive index data, resulting in high size resolution. Furthermore, an assessment of the surface functional groups of the AgNPs that were synthesized was conducted via Fourier transform infrared spectroscopy (FTIR) utilizing the KBr-disc method within the 400-4000 cm −1 range.

Experimental Field Design and Data Recorded
The field study on Asclepias curassavica plants was conducted over the course of two successive growing seasons, 2020 and 2021, at the Nursery of Department of Floriculture, Ornamental Horticulture and Garden Design, Faculty of Agriculture, Alexandria University, Egypt. The plant with its voucher number Z0001 was identified by Dr. Hany M. El-Naggar (Department of Floriculture, Ornamental Horticulture and Garden Design, Faculty of Agriculture (El-Shatby), Alexandria University, Alexandria).
Clay and sand (2:1 v/v) were used as the growing media for A. curassavica plants, and two amounts of compost were applied when the soil was prepared for the two seasons, as shown in Table 9. AgNPs were sprayed on the plants three times: on the first of May, the first of June, and the first of July for the two seasons. The concentrations used were 0, 10, 20, and 30 mg/L. Table 10 displays the results of the compost's chemical analysis.  In both seasons, measurements were taken of the plant's height (cm), diameter (cm), number of branches/plant, leaf area, total fresh weight (g), total dry weight (g), total chlorophyll (SPAD unit), and the percentage of extracts.
The extraction yield of A. curassavica plants was calculated using the following equation: extraction yield (%) = W1/W2 × 100, where W1 is the mass of leaf crude extract and W2 is the mass of the leaf sample [115].

Preparation of Plant Methanol Extracts
A. curassavica leaves were air dried at room temperature and transferred to powder using a grinder. About 50 g from the powdered leaves was extracted by the methanol solvent (150 mL) for 72 h at room temperature. The solvent was removed and the extracts were concentrated and collected in separate bottles and stored at 4 • C until further analysis [116].
Antibacterial activity was determined using the disc diffusion method [117,118], where the autoclaved filter paper discs 5 mm in diameter were used and each disc received 40 µL of the prepared concentrations (4000, 2000, 1000, and 500 µg/mL). The minimum inhibitory concentrations (MICs) were determined by serial dilution of the extracts ranging from 15 to 4000 µg/mL [119]. Negative (10% DMSO) and positive (gentamicin 20 µg/disc) controls were used, and all tests were performed in triplicate.

HPLC Analysis of Phenolic and Flavonoid Components
The phenolic components from the methanol extracts of A. curassavica leaves were categorized by HPLC (Agilent 1100, USA). A binary LC pump, a UV/Vis detector, and a C18 column (125 mm, 4.60 mm, 5 µm) make up this apparatus. The Agilent Chem-Station was used to acquire and analyze chromatograms. A gradient mobile phase of two solvents-Solvent A (MeOH) and Solvent B [Acetic acid in H 2 O (1:25)]-was used to separate phenolic acids. The gradient program began with 100% B and remained there for 3 min. This was followed by 5 min of 50% eluent A, 2 min of 80% eluent A, 5 min of 50% eluent A, 2 min of 80% eluent A, 5 min of 50% eluent A, 5 min of 50% eluent A, and 5 min of detection wavelength at 250 nm. As a result, the phenolic components were arranged in order to authenticate standard components by this mobile phase [120,121]. For the flavonoid compounds, HPLC (Agilent 1100), composed of two LC pumps, a UV/Vis detector, and C18 column (250 mm × 4.6 mm, 5 µm), was used. The mobile phase was acetonitrile (A) and 0.2% (v/v) aqueous formic acid (B) with an isocratic elution (70:30) program. The detection wavelength was set at 360 nm [121].

Statistical Analysis
The experiment was statically analyzed using CoStat program ver., 6.303 (CoHort software, Monterey, CA, USA). A completely randomized design [122] was performed and the means were equated by the Least Significant Difference (LSD) at 0.05 level of probability [123]. The data were expressed as means ± 2SD values and were deemed statistically significant when p ≤ 0.05.

Conclusions
The findings of the current study show that the interaction of compost and AgNPs applications had a positive effect on the vegetative parameters of A. curassavica plants, including plant height (cm), plant diameter (cm), branch number/plant, leaf fresh weight (g), leaf dry weight (g), and leaf area (cm 2 ), gradually increasing with concentration compared to untreated plants. The chemical constituents of A. curassavica plants, such as their chlorophyll content, leaf methanol extract percentages, phenolic compounds, and flavonoid compounds, were also impacted by the treatments. Generally, the best outcomes were achieved with for the majority of the assessed parameters. We recommend that the plants treated with 50% compost containing 20 or 30 mg/L AgNPs be employed in field experiments at a wide scale and in subsequent research.