Can Foliar-Applied Omeprazole Improve the Yield, Assimilation, Recovery and Nitrogen Use Efficiency in Bean Plants?

Abstract

The low efficiency of nitrogen (N) fertilizers is a frequent problem in agriculture that impacts the environment. Omeprazole (OMP) has been reported to promote N uptake and assimilation in tomato, basil, and corn. However, information about the effect of omeprazole on N assimilation, recovery, and N use efficiency parameters for bean plants is limited. Therefore, the objective of the present study was to determine the effect of foliar applications of OMP at 0, 1, 10, and 100 µM on nitrogen assimilation, growth, yield, nitrogen use efficiency parameters, and recovery percentage in green bean plants. Green bean plants cv. Strike grown in pots were used. Biomass, yield, nitrate reductase activity, photosynthetic pigments concentration, soluble amino acids and protein concentrations, total nitrogen concentration, nitrogen use efficiency parameters, and nitrogen recovery were analyzed. The results obtained indicate that the application of OMP at 1 µM increased yield and biomass, promoted N assimilation through higher NR enzyme activity, higher amino acid concentration, higher N use efficiency coefficient, and allowed a more efficient nitrogen recovery percentage.

1. Introduction

The low efficiency of nitrogen (N) fertilizers in agriculture has led to an intensified use with detrimental effects on the environment [1]. Depending on crop conditions, about 50% of the applied N is lost by volatilization or leaching and is released to the atmosphere or deposited in water bodies [2]. In addition, agricultural soils with appropriate ammonium (NH₄⁺) or nitrate (NO₃⁻) content are uncommon, so external input is necessary to satisfy production demand [3]. Therefore, increasing nitrogen use efficiency (NUE) is a crucial objective to achieve sustainable food production [4,5].

Generally, NUE has been described as the amount of N applied to crops that is assimilated by plants and transformed into plant mass [6]. It has been further divided into two terms that refer to central processes in its assimilation. The capacity of roots to absorb N from the soil is called absorption efficiency (NUpE), and the capacity to mobilize it to the different plant organs is called utilization efficiency (NUtE) [7].

A novel alternative that has shown positive results in the efficient use of nutrients in plants is the application of low-weight molecules such as omeprazole [8,9]. Omeprazole (OMP) (C₁₇H₁₉N₃O₃S) is a proton pump inhibitor in humans, with influence on other physiological processes in plant species [10]. Previous studies have proven that OMP application in tomato stimulates root and plant growth and enhances photosynthesis [11]. Also, it improves potassium and nitrate uptake in basil plants [12,13]. Moreover, it allowed for an increase in N assimilation in maize seedlings through changes in nitrate reductase activity, primary metabolism, and gene expression [10]. Also, it increased shoot and root growth, chlorophyll concentration, photosynthetic rate, and photosynthetic gas exchange in peppermint plants [14].

However, although there is evidence of increased NUE with the use of OMP in other crops, the pathways responsible for these responses in green bean (Phaseolus vulgaris L.) plants are still unknown. Therefore, the objective of the present study was to determine the effect of foliar application of OMP on nitrogen assimilation, growth, yield, and NUE parameters in green bean plants cv. Strike.

2. Materials and Methods

2.1. Crop Management

The experiment was conducted at the facilities of the Centro de Investigación en Alimentación y Desarrollo, in Cd. Delicias, Chihuahua, Mexico, during the months of September and October 2022, under shade net conditions. Seeds of green bean cv. Strike provided by Hydro Environment^® (Tlanepantla, México) were used. Seeds were directly sown on 13 L plastic pots filled with vermiculite and perlite in a 2:1 (v/v) ratio. During the experiment, the plants were irrigated with a standard Hoagland nutrient solution, adapted to the physiological needs of beans by Sánchez et al. [15], and 500 mL of the pH 6 ± 0.1 of nutrient solution were applied per pot every 48 h until the flowering stage (32 days after sowing (DAS)), and an amount of 1 L was added until harvest (53 DAS).

2.2. Experimental Design

A completely randomized design with a unifactorial arrangement and 4 levels was used. The factor to be evaluated was the foliar application of OMP and the levels were 0, 1, 10, and 100 µM. There were 4 treatments and 6 replications per treatment. The experimental unit was one plant per pot. The model used for the experiment was Yij = µ + τi + εij, where Yij was the response variable, under the effect of the i-th treatment and the j-th repetition; µ was the overall mean; τi was the effect of the i-th treatment; and εij was the experimental error.

2.3. Plant Sampling

Once the plants reached physiological maturity at 53 DAS, the plant material was harvested. The collected material was washed with distilled water to remove residues and finally separated into organs (root, stem, leaves, and fruit). The samples were divided into fresh and dry material. The fresh material was used for in vivo analyses, which included yield, nitrate reductase activity, photosynthetic pigments and soluble amino acids and protein. The dry material was used for the quantification of biomass, total nitrogen, and efficiency parameters.

2.4. Plant Analysis

2.4.1. Total Biomass and Yield

One plant was randomly selected from each pot and weighed fresh using a compact balance (A&D Co., Ltd., EK-120, Tokyo, Japan). Subsequently, the plant was dissected into leaves, stem, pods, and root, and each organ was weighed fresh. Yield was expressed as the fresh weight of pods per plant (g plant⁻¹ FW).

The obtained organs were rinsed three times in distilled water and dried on filter paper at room temperature for 24 h. After this period, the plant material was dried inside a 13.9-cubic-foot forced-air laboratory oven (Shel-Lab 1380FX, Cornelius, OR, USA) at 70 °C for 24 h. After the samples lost moisture, they were weighed with an electronic analytical balance (A&D Co., Ltd., HR-120, Tokyo, Japan). Total biomass was expressed as the sum of the dry weight of the four plant organs (g plant⁻¹ DW). Finally, the samples were ground and stored for quantification of total nitrogen.

The plant that was not subjected to drying was divided into leaves, stem, fruit, and root and used in vivo for the quantification of nitrate reductase activity, photosynthetic pigments, amino acids, and soluble proteins.

2.4.2. “In Vivo” Nitrate Reductase Enzyme Activity (NR) (E.C. 1.7.1.1)

Nitrate reductase enzyme activity was quantified using the method described by Sánchez et al. [16]. In detail, 0.25–0.5 g of leaf discs were weighed and infiltrated with 10 mL of a 100 mM P-buffer solution (18.21 g of Na₂HPO₄·12H₂O dissolved in 1 L of distilled water, adjusted to pH 7.5 with a solution of 13.60 g of KH₂PO₄ dissolved in 1 L of distilled water) for endogenous activity and with 100 mM buffer-P at pH 7.5 with 50 mM of KNO₃ for the activity infiltrated with NO₃⁻. The samples were infiltrated under vacuum at 0.8 bar for 10 min (NAPCO 5851 vacuum oven, Winchester, VA, USA) and incubated in the dark at 30 °C for 1 h (WIG-50 digital incubator, DAIHAN SCIENTIFIC, Seoul, Republic of Korea). The samples were then subjected to a water bath at 100 °C for 15 min. A 1 mL aliquot was then extracted and mixed with 2 mL of 1% sulfanilamide (1 g of sulfanilamide dissolved in 100 mL of distilled water and HCl in a 4:1 ratio (v/v)). Then, 2 mL of N-(1-naphthyl) ethylenediamine dichlorohydrate at 0.02% was added (20 mg of NNEDA dissolved in 100 mL of distilled water). The reaction mixture was measured on a UV-visible spectrophotometer at a wavelength of 540 nm (Thermo Fisher Scientific, GENESYS™ 10S, Madison, WI, USA). The results were expressed a µM NO₂⁻ formed g⁻¹ FW h⁻¹.

2.4.3. Photosynthetic Pigments

The concentrations of chlorophyll a and b and of carotenoids were determined by the method described by Wellburn [17]. Ten leaf discs of 7 mm diameter were weighed and infiltrated with 10 mL of methanol (CH₃OH). The samples were sealed and allowed to stand in the dark for 24 h. After that time, the absorbance of the samples was measured at wavelengths of 470, 653, and 666 nm for carotenoids, chlorophyll b, and chlorophyll a, respectively, using a UV-visible spectrophotometer (Thermo Fisher Scientific, GENESYS™ 10S, Madison, WI, USA). The pigment concentrations were expressed as µg cm² FW and were calculated using the following formulas:

Chl a = (15.65 × abs 666) × (7.34 × abs 653)
(Chl a × V × W1)/(W2 × (π × r²) × n)

(1)

Chl b = (27.05 × abs 653) − (11.21 × abs 666)
(Chl b × V × W1)/(W2 × (π × r²) × n)

(2)

Carotenoids = ((1000 × abs 470) − (2.86 × Chl a) − (129.2 × Chl b))/221
(Carotenoids × V × W1)/(W2 × (π × r²) × n)

(3)

where V: final volume; W1: weight per leaf disc; W2: total weight of leaf discs; r: radius of the leaf discs; n: number of leaf discs.

2.4.4. Soluble Amino Acid and Soluble Protein Concentrations

A 0.5 g volume of plant sample from leaf blade was homogenized with 5 mL of 50 mM phosphate buffer, pH 7 at 4 °C (solution of 6.8 g of K₂HPO₄ dissolved in 1 L of distilled water, adjusted to pH 7 with a solution of 8.81 g of KH₂PO₄ dissolved in 1 L of distilled water). The sample was filtered through 4 layers of gauze and centrifuged at 1000 rpm for 15 min in a refrigerated centrifuge at 4 °C (Allegra™, 64R Centrifuge, Beckman Coulter, Brea, CA, USA). The supernatant was used for the determination of amino acid and soluble protein concentrations by the methods described by Yemm et al. [18] and Bradford [19], respectively.

For the quantification of soluble amino acids, a 100 µL aliquot of supernatant was mixed with 1.5 mL of ninhydrin reagent (2 g of ninhydrin dissolved in 50 mL of ethylene glycol (CH₂OHCH₂OH), mixed with 80 mg of stannous chloride (SnCl₂·2H₂O), dissolved in 50 mL of 200 mM citrate buffer at pH 5 (solution of 59. 41 g of tribasic sodium citrate dihydrate (C₆H₅Na₃O₇·2H₂O), dissolved in 1 L of distilled water, and buffered to pH 5 with a solution of 38.81 g of anhydrous citric acid (C₆H₈O₇)). The sample was shaken and subjected to a water bath at 100 °C for 20 min. The samples were then subjected to a water bath at 4 °C for 30 min and reacted with 8 mL of 1-propanol (C₃H₈O) at 50% (v/v). Finally, the samples were measured at 570 nm using a UV-visible spectrophotometer (Thermo Fisher Scientific, GENESYS™ 10S, Madison, WI, USA) versus a glycine standard curve. The results were expressed as (mg g⁻¹ FW).

For soluble protein quantification, a 20 µL aliquot of the centrifuged supernatant was taken and mixed with 1 mL of the Bradford Quick Start™ Protein Assay Kit dye reagent (Bio-rad, Hercules, CA, USA). Samples were shaken and allowed to stand for 15 min. Finally, they were measured at an absorbance of 595 nm through a UV-visible spectrophotometer (Thermo Fisher Scientific, GENESYS™ 10S, Madison, WI, USA) against a bovine serum albumin (BSA) standard curve. The curve was prepared by taking 20 µL of each of the standards from the Bradford Quick Start™ protein assay kit at concentrations of 0.125, 0.25, 0.5, 0.75, 1, 1.5, and 2 mg mL⁻¹ of BSA and distilled water for the blank. The results were expressed as (mg g⁻¹ FW).

2.4.5. Total Nitrogen Concentration

For the quantification of total nitrogen, an organic elemental analyzer was used (Thermo Fisher Scientific, FLASH 2000, Waltham, MA, USA), with the methodology described by Dumas [20] and adapted by Krotz and Giazzi [21] for plant material was used as a basis. In detail, 0.3 mg of the ground plant material (leaf, stem, fruit, and root) was weighed on a soft tin microcontainer in an ultra-microbalance (Mettler Toledo, XP6 Excellence Plus XP, Columbus, OH, USA), to which 9 mg of vanadium pentoxide (V₂O₅) was added and subsequently sealed. The sealed capsules were placed inside the automatic sampler carousel for analysis. The results were expressed as percentage of total nitrogen (%).

2.4.6. Nitrogen Use Efficiency Parameters

Calculations of nitrogen use efficiency (NUE) parameters were based on the methodology of Moll et al. [22], with adaptations suggested by Congreves et al. [23]. Once the total N concentration was obtained, it was multiplied by 10 to obtain the total nitrogen content (TNC). The TNC was expressed as (mg g⁻¹ DW).

TNC = Total nitrogen concentration × 10

(4)

To obtain the amount of total nitrogen accumulated (TNA), the total biomass was multiplied by the TNC. The TNA was expressed as (mg).

TNA = Total biomass × TNC

(5)

For the calculation of nitrogen utilization efficiency (NUtE), total biomass was divided by TNC. The value of NUtE was expressed as (g DW mg⁻¹ N).

NUtE = (Total biomass)/TNC

(6)

The nitrogen uptake efficiency (NUpE) value was obtained by dividing TNA by the root biomass in dry weight and was expressed as (mg N g⁻¹ DW).

NUpE = TNA/(Root biomass)

(7)

Finally, the nitrogen use efficiency index (NUE) was obtained by dividing the dry weight of the pods by TNA. NUE was expressed as (mg DW).

NUE = Dry weight of pods/TNA

(8)

2.4.7. Nitrogen Recovery Percentage

The determination of the percentage of N recovered was based on the methodology described by Westermann et al. [24], with modifications suggested by Martin [25]. The total liters of nutrient solution applied to the crop were considered to calculate the amount of N applied. The total amount of nutrient solution per plant (9 L) was multiplied by the ammonium nitrate concentration (NH₄NO₃) contained in 1 L. The result in milligrams was multiplied by a factor of 0.35, corresponding to the total N in the NH₄NO₃. The result was expressed as mg of N applied. To determine the percentage of N recovered, the TNA (mg N) was divided by mg N applied. The result was multiplied by 100 and expressed as a percentage (%).

Total N applied = (Total solution applied (L) × 4.53 g L⁻¹) × 0.35

(9)

Percentage of N recovered = TNA/(Total N applied)

(10)

2.5. Statistical Analysis

Once the data were obtained, they were subjected to a Shapiro–Wilk test to check the normality of the distribution. Additionally, they were subjected to a Bartlett’s test to test for the homogeneity of variances. Once the assumptions had been checked, the data were subjected to a one-way analysis of variance and a test of separation of means using the LSD Fisher test. The SAS 9.0 statistical package was used for the statistical analyses. Different letters showed statistically significant differences according to the LSD Fisher test (p ≤ 0.05). Significance level: *: p ≤ 0.05; **: p ≤ 0.01; ***: p ≤ 0.001.

3. Results

3.1. Total Biomass and Yield

The efficacy of the OMP doses applied in this experiment was reflected in the accumulation of total biomass (p < 0.01), whose value increased significantly with respect to the control with the three doses used (Figure 1). Furthermore, despite the fact that the highest amount of biomass was presented in the OMP 100 treatment, with an increase of 32% with respect to the control, no significant differences were found between the doses of 1, 10, and 100 µM of OMP, so that the lower dose can be an effective alternative to promote biomass accumulation.

Pod yield was stimulated by the application of OMP on green bean plants (p < 0.001). That is, all doses achieved an increase in pod production (Figure 1b). However, the highest yield was obtained in the OMP 1 treatment, with an increase of 171% with respect to the control. Finally, a downward trend was observed as the dose of OMP applied increased.

3.2. “In Vivo” Nitrate Reductase Enzyme Activity (NR) (E.C. 1.7.1.1)

In our experiment, endogenous (p < 0.01) and NO₃⁻-induced (p < 0.001) NR activity was affected at different levels depending on the dose of OMP applied. The highest endogenous NR activity was presented in the OMP 10 treatment, which was able to increase by 51% relative to the control (Figure 2a). On the other hand, the highest NO₃⁻-induced NR activity was obtained in the control treatment with no statistical difference compared to OMP 10, which increased by 49% relative to OMP 100 and 30% relative to OMP 1 (Figure 2b).

3.3. Photosynthetic Pigments Concentration

Regarding the concentration of photosynthetic pigments, the application of OMP at a dose of 100 µM obtained the best results (

Table 1. Effect of foliar OMP applied to green bean plants cv. Strike on photosynthetic pigment concentration. Different letters indicate significant statistical differences according to the LSD Fisher test (p ≤ 0.05).

	Chlorophyll a	Chlorophyll b	Carotenoids
Treatment
CONTROL	3.28 ± 0.35 ab	1.4 ± 0.15 b	0.42 ± 0.06 bc
OMP 1	3.14 ± 0.21 b	1.4 ± 0.13 b	0.47 ± 0.03 b
OMP 10	2.99 ± 0.23 b	1.33 ± 0.10 b	0.39 ± 0.03 c
OMP 100	3.65 ± 0.41 a	1.59 ± 0.16 a	0.55 ± 0.06 a
p ≤ 0.05	***	*	***

Pigment concentration is expressed as µg cm² FW. Significance level: *: p ≤ 0.05; 0.01; ***: p ≤ 0.001.

). The highest concentration of chlorophyll a (p < 0.01) was present in the OMP 100 treatment, which was higher by 22% and 16% with respect to OMP 10 and OMP 1, but with no difference compared to the control. As for chlorophyll b (p < 0.05), the OMP 100 treatment showed the highest concentration, with an increase of 14% with respect to the control. A similar trend was observed for carotenoid concentration (p < 0.001), where the OMP 100 treatment was the most favored, with an increase of 31% over the control.

3.4. Soluble Amino Acid and Soluble Protein Concentrations

Regarding the concentration of soluble amino acids and soluble protein analyzed in our study, the application of OMP stimulated their production at low doses in bean plants (Figure 3). In other words, the highest concentration of soluble amino acids (p < 0.01) was presented in the OMP 1 treatment, with an increase of 14% with respect to the control. On the other hand, the OMP 10 treatment presented the highest concentration of soluble proteins (p < 0.07), with an increase of 18% with respect to the control.

3.5. Total Nitrogen Concentration

In our study, an increase in N concentration (p < 0.001) was observed as OMP was applied (Figure 4). However, the total N concentration was not statistically different between the 1, 10, and 100 µM doses. Finally, the 1 µM dose could be more effective by reducing the OMP dose 100 times and increasing the N concentration by 13%.

3.6. Nitrogen Use Efficiency Parameters

The nitrogen use efficiency, estimated through four different parameters, obtained the best results with the 1 µM dose of OMP in green bean plants (Figure 5). The highest amount of total nitrogen accumulated (p < 0.001) was found in the OMP 100 treatment, with an increase of 52% compared to the control (Figure 5a). However, no significant differences were found between the 1, 10, and 100 µM doses.

With respect to NUpE (p < 0.06), the treatment with the most favorable increase was OMP 10, with an increase of 16% compared to the control and OMP 100 but no difference compared to OMP1. In the case of (NUtE) (NS), no differences were observed between treatments. Finally, the highest nitrogen use efficiency index (p ≤ 0.05) was obtained in the OMP 1 treatment, which was 82% higher compared to the control.

3.7. Nitrogen Recovery Percentage

Finally, the effectiveness of the OMP doses used in this experiment in the recovery of nitrogen percentage (p < 0.01) had a positive effect that did not depend on the dose (Figure 6). The highest percentage recovery was found in the OMP 100 treatment, with an increase of 52% with respect to the control. However, no significant statistical difference was found with respect to the 1 and 10 µM doses, with both options being viable with a considerable decrease in OMP applied.

4. Discussion

Previous studies have documented the effectiveness of omeprazole application to improve growth, development, and nitrogen assimilation in several crops such as corn, tomato, basil, and mint. In our experiment, the total biomass of bean plants showed a similar increase at both low and high doses (Figure 1a). This behavior has been previously described by several authors, who suggest that OMP-treated plants show increased plant growth and a prolonged plant growth stage due to the interaction of OMP with endogenous auxin [14]. For example, Elansary and El-Abedin [14] have reported a 15% increase in the dry weight of mint plants treated with OMP at 100 µM. Carrillo et al. [26] have reported increases of 14% in the shoot dry weight and 27% in the root dry weight of basil plants treated with OMP at 10 µM. Likewise, Carrillo et al. [27] have found 7% increases in the dry biomass of lettuce plants treated with 10 µM OMP. Also, Rouphael et al. [11] have reported that, under salinity conditions, the application of 100 µM OMP increased the dry weight of tomato plants by 43%.

Crop yield is influenced by growth conditions and nutritional status, among other factors [28]. Therefore, yield measurement can be indicative of the effectiveness of the treatments applied. Regarding pod yield, the results are similar to those found by several authors in other plant species. Rouphael et al. [11] have reported yield increases of 54% and 39% in tomato plants when omeprazole was applied at doses of 10 and 100 µM, respectively. However, in our study, the higher dose of OMP resulted in a decrease in yield. That is, the highest yield was obtained at the 1 µM and 10 µM dosses and as the dose was increased to 100 µM, the value decreased with a drop of 37%. This could indicate a negative effect of OMP at high concentrations on pod production for bean plants. In addition, the national average yield in Mexico for green beans is around 51.8 g plant⁻¹ FW [29]. The treatment with the highest pod yield (OMP 1) was below that average by 29%; however, the treatment without OMP application was drastically reduced by 249%. This indicates that OMP at low doses can be a viable alternative to increase crop yield.

The most limiting step for N assimilation in plants is the reduction of NO₃⁻ to NO₂⁻, which is carried out by the enzyme NR [30]. In addition, the drastic effect on the increase in plant biomass may be related to a correct supply of N-assimilates, which starts with this process. The 10 µM dose was optimal for increasing NR activity, but it was not statistically different to the 1 µM dose (Figure 2a). These results are identical to those reported by Van Oosten et al. [10], who found 48% increases in NR enzyme activity in maize seedlings treated with OMP at a 10 µM dose and an 18% at 1 µM dose. The improvement in enzyme activity is possibly due to the increase in the activation state of the enzyme. Likewise, among the 1 and 10 µM doses, the one that showed the lowest activity upon induction with NO₃⁻ was OMP 1, which may suggest that the enzyme was saturated with substrate and therefore at its maximum activity capacity. The results suggest that the application of OMP contributes to maintaining a specificity of the NR enzyme to the substrate and thus a constant catalytic activity [10].

As indicated by Van Oosten et al. [10], the addition of omeprazole can show inhibitory effects at doses 100 and 1000 times higher than 1 µM. Moreover, these inhibitory effects are mainly present in the parameters of nitrogen metabolism. The downward trend observed in yield, NR activity, amino acid and soluble protein concentrations, NUpE, and NUE at the highest doses of OMP applied in this experiment could be explained by hormone-driven regulation. Recently, it has been reported that OMP treatment at low doses boosts endogenous auxin synthesis; however, at high doses, it is possible that it may cause a reduction in fresh weight and main root length. However, more studies are needed on the mechanism of omeprazole inhibition at high doses, since growth regulation may respond to the homeostasis of several hormones and not only auxin [31]

Previously, several authors have used the concentration of photosynthetic pigments in leaves as a valuable indicator of physiological status in plants [32]. In the present study, chlorophyll a, chlorophyll b, and carotenoids were seen at higher values with the highest dose of OMP (Table 1). A deficiency of photosynthetic pigments may be related to a nutritional imbalance of N in leaves. Moreover, since photosynthetic pigments are readily available nitrogenous compounds, they can be used as an intracellular N reserve to support growth in case of limiting factors [33]. This mechanism was possibly manifested in the OMP 100 treatment, where chlorophyll a and b and carotenoid concentrations were stimulated and, in addition, the highest biomass was obtained, reinforcing the idea that the application of OMP at high concentrations prolongs the vegetative cycle of plants. On the other hand, OMP has been described as responsible for interacting with endogenous abscisic acid (ABA) levels in plants [10]. The prolongation of the vegetative period and the lack of induction in pod formation and filling was possibly caused by the high doses of OMP that induced a higher concentration of carotenoids (Table 1). Thus, as the ripening stage progresses, ABA levels drop, so carotenoid concentration decreases [34]. This condition may have occurred in the OMP 1 treatment, which achieved a higher yield, as opposed to OMP 100, which only achieved a higher biomass accumulation. Finally, further studies on the role of OMP in the biosynthesis of ABA and carotenoid-derived compounds are needed.

Plant development and growth can be related to an adequate amino acid content as these are the key products needed to form proteins, nucleic acids, and other cellular compounds [35]. Overall, OMP treatment at the 1 µM dose was notable for its higher concentration of soluble amino acids and high concentration of soluble proteins (Figure 3). The key to the mechanism through which OMP acts to increase plant growth and yield is possibly in the amino acid content. The treatment with the highest yield was the same treatment with the highest concentration of soluble amino acids (Figure 1b and Figure 3a). As described by several authors previously, OMP enhances plant growth through its interaction with the auxin synthesis process [10]. Endogenous auxin synthesis starts from intracellular amino acid content, specifically tryptophan as a precursor [36]. One of the mechanisms that probably favored both biomass accumulation and higher yield in OMP 1 was the accumulation of soluble amino acids, which facilitated the transport of assimilates to the source organs.

Finally, total nitrogen concentration and nitrogen use efficiency parameters can be indicators of the mechanisms that favor high yield and plant biomass creation in bean plants [2]. Similarly, parameters which are commonly used to estimate the efficiency of fertilizers used for crop production are uptake efficiency (NUpE), utilization (NUtE), and nitrogen use efficiency (NUE) [37]. It is possible that the reason why there were no significant differences in the utilization coefficient (NUtE) is that all treatments were under optimal N nutrition, so their performance was normal. However, the highest coefficient of efficiency (NUE) was obtained with the lowest dose of OMP (1 µM) (Figure 5d). This result could indicate that the most favorable dose for agronomic, biochemical, and resource use efficiency parameters is the 1 µM dose.

It is important to know the percentage of N recovery in plants as a complement to the parameters of NUE, since sometimes systems with high N inputs tend to decrease yields, contrary to what might be thought [38]. Likewise, the lowest dose of OMP contributed to recovering about 10% of the N applied to bean plants, competing with doses 10 and 100 times higher, which could be reflected in the higher yields and a considerable decrease in inputs (Figure 7).

5. Conclusions

According to the results obtained, it is concluded that the foliar application of OMP at a dose of 1 µM is considered optimal to increase growth, pod production, soluble amino acids, and nitrogen use efficiency of green bean plants cv. Strike. In addition, OMP application was able to promote N assimilation through increased NR enzyme activity, higher N concentration, and products such as amino acids and proteins. Also, the application of OMP at 100 µM dose increased the photosynthetic pigments. Finally, the results suggest that OMP could be a viable alternative for incorporation in agriculture and increasing crop production in a sustainable way.