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Horticulture International Journal

Research Article Volume 6 Issue 2

Bacillus thuringiensis and Micromonospora echinosporaon growth of Phaseolus vulgaris

Adilene Velázquez-Medina, Juan Luis Ignacio De la Cruz, Juan Manuel Sánchez-Yáñez

Environmental Microbiology Laboratory, Chemical Biological Research Institute, Ed-B3; Michoacana University of San Nicolás de Hidalgo, México

Correspondence: Juan Manuel Sánchez-Yáñez, Environmental Microbiology Laboratory, Chemical Biological Research Institute, Universidad Michoacana de San Nicolas de Hidalgo, Francisco J Mujica S/N Col Felicitas del Rio, CP58,000 Morelia, Mich, México, Zip Code 58000

Received: April 20, 2022 | Published: May 5, 2022

Citation: Velázquez-Medina A, Luis Ignacio-De la Cruz J, Manuel Sánchez-Yáñez J. Bacillus thuringiensis and Micromonospora echinospora on growth of Phaseolus vulgaris. Horticult Int J. 2022;6(2):89-93. DOI: 10.15406/hij.2022.06.00247

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Abstract

The well-known bacteria genus called as Bacillus thuringiensis (Bt) is recognized for being used in the biological control of insect pests in agriculture. However, there is little information on the effect of Bt as a plant growth promoter and in interaction with Micromonospora echinopora, which, being an endophyte, could improve the response of Phaseolus vulgaris with NH4NO3 atreduced at 30%of common recommended without risk of affecting plant health or yield.The objective of this work was to analyze the response of P. vulgaris to Bt and M. echinospora with NH4NO3 at 30% of recommended dose. The experiment was conducted under a randomized block design, using the response variables: germination percentage, phenology and biomass. The experimental data were analyzed by ANOVA/Tukey HSD (P<0.05). In the results, it was found that B.thuringiensis induced in P. vulgaris a yield of 3.2Ton/Ha, while with M. echinospora 3.6Ton/Ha was reached, with NF reduced at 30%, while it was shown that B.thuringiensis improved the yield with M. echinospora with 4.0Ton /Ha, values with statistical difference compared to the 2.8 Ton/Ha of P. vulgaris without B.thuringiensis or M. echinospora used as relative control with 100% of the NF.Concluded that B. thuringiensis is not only useful in biological control but that it can be an excellent growth promoter that can be improved with M. echinospora, another option for the sustainable production of P. vulgaris.

Keywords: legume, soil, hyperfertilization, beneficial endophytic bacteria, plant health.

Introduction

The healthy growth of Phaseolus vulgaris (bean) requires nitrogen fertilizer (NF) commonly as a NH4NO3, which at high doses causes loss of soil productiveness due to rapid mineralization of organic matter,1-3 An natural and ecological alternative solution to optimization of NF in P. vulgaris from seed inoculation with Bacillus thuringiensis and Micromonospora echinospora, genera and species of plant growth-promoting endophytic bacteria (PGPEB)which convert exudates from the seed spermosphere and inside the roots into plant growth promoting substancesor phytohormones that accelerate germination and induce a denser root system for the absorption and optimization of the NF applied at doses lower than those recommended, without affecting healthy plant growth.4-7 Generally, for P. vulgaris, inoculants based on Rhizobium etli are recommended, a symbiote of this class of legumes, which is dependent on the variety of P. vulgaris and/or the soil. They may not be infective and effective in facilitating healthy growth at doses of NF for sustainable production. Based in some reports that showed that other bacteria could be apply in P. vulgaris and other legumescould be inoculated with B. megaterium8 or with actinomycetes likeStreptomyces flavoviridis a.9 Therefor the objective of this research was to analyze the response of P. vulgaris to B. thuringiensis and M. echinospora with NH4NO3 at 30%.

Material and methods

This research was carried out in the greenhouse of the Environmental Microbiology laboratory, Instituto de Investigaciones Químico-Biológicas (IIQB) of the Universidad Michoacana de San Nicolás de Hidalgo (UMSNH), Morelia, Mich, Mexico, with the average microclimatic conditions were: temperature of 23.2°C, luminosity of 450μmol-m-2s-1 and 67% relative humidity. In this trial, a non-sterile soil collected from the municipality of Salvador Escalante Michoacán, Mexico, with a silty clay loam texture with 10.44% organic matter and pH of 5.75 moderately acidic according to NOM-021-RECNAT-2000 was used.10 20 mesh and solarized at 70°C/48h to minimize pests and diseases, then 1.0kg of soil was placed in the top container of the Leonard jar (Figure 1), while NF in a mineral solution or water in the reservoir at the bottom, P. vulgaris seeds were disinfected with 5% NaClO/5min and washed 5 times with sterile drinking water, then disinfected in 70% alcohol/ 5min and washed 5 times with sterile drinking water, then B. thuringiensis isolated from soil rich in organic matter was activated in nutrient broth with the following chemical composition (g/L): casein peptone 5; yeast extract 3; distilled water, adjusted the culture medium to pH 6.8±0.2; with the antifungal Tecto®60 (Syngenta), while M. echinospora isolated from nodules of M. sativa was propagated on avocado pit agar with the following chemical composition (g/L): avocado pit 10.0, casein peptone 5.0, yeast extract 1.3, K2HPO4 0.17, KH2PO4 2.61, MgSO4 1.5, NaCl 0. 9, CuSO4 0.05, bromothymol blue 10% (w/v) 10ppm, trace element solution 1.0mL, detergent solution 2.5mL at 10%, antifungal Tecto®60 1.0mL at 10%, 1.0mL, bacteriological agar 18.0, at pH 7.5, both bacterial genera were incubated at 30°C/72h. Then for every 10 P. vulgaris seeds, 1.0mL of B. thuringiensis was used at a density of 4.6x106CFU/mL and M. echinospora at a density of 3.5x106 propagule forming units/mL. Table 1 describes the experimental design with 2 controls and 6treatments with 6 replicates: P. vulgaris irrigated with water or absolute control (AC); P. vulgaris fed with NFat 100%or relative control (RC); P. vulgaris with B. thuringiensis and/or M. echinospora with 30% reduced NF in a mineral solution with the following chemical composition (g/L): NH4NO3 10.0, K2HPO4 2.5, KH2PO4 2.0, MgSO4 1.0, NaCl 0.1, CaCl2 0.1, trace FeSO4, trace element solution 10.0mL, adjusted to pH 6.5-6.8. The NF was applied every third day at 80% field capacity.11 The response variables were: percentage (%) of germination and days of emergence; phenology: plant height (PH), root length (RL); biomass: aerial fresh weight (AFW) and root fresh weight (AFW), and aerial dry weight (ADW) and root dry weight (RDW) at seedling, flowering and physiological maturity stages and yield, the experimental data were validated with the statistical program ANOVA/Tukey HSD P<0.05 with Statgraphics Centurion.13

Figure 1 Leonard's jar design.12

*Phaseolus
Vulgaris

Water

NH4NO3

Bacillus thuringiensis

Micromonospora echinospora

Absolute control (AC)

+

-

-

-

Relative control (RC)

-

100%

-

-

Treatment 1

-

30%

+

-

Treatment 2

-

30%

-

+

Treatment 3

-

30%

+

+

Table 1 Experimental design to analyze the growth of Phaseolus vulgaris to Bacillus thuringiensis and Micromonospora echinospora with NH4NO3 reduced at 30%

*Number of repetitions = 6; (+) added; (-) not added.

Results

In Table 2 shows the percentage and days of emergence of P. vulgaris seeds with B. thuringiensis and/or M. echinospora and NH4NO3 at 30%, emerged 3days after sowing, or 94% germination a numerical value stadistically different compared to 5days of emergence or 83% of P. vulgaris withoutB. thuringiensis/M. echinospora and NH4NO3100% or relative control (RC).

Treatment/P. vulgaris*

Percent (%) germination

                 Days emergence

Irrigated with water (AC)

77d**

**5b

with NH4NO3 at 100% (RC)

83b

5b

B. thuringiensis +NH4NO3at 30%

94a

3a

M. echinospora + NH4NO3at
30%

91a

3a

B. thuringiensis/M. echinospora +NH4NO330%

94a

3a

Table 2 Percentage and days to emergence of Phaseolus vulgaris with Bacillus thuringiensis and Micromonospora echinospora andNH4NO3 reduced at 30%

*n=6, ** Different letters indicate statistical difference by ANOVA/Tukey (P>0.05).

In Figure 2 shows that the seed of P. vulgariswith NH4NO3 at 30% emerged 5 days after sowing, due toB. thuringiensis /M echinosporaby phytohormons from organic compound from the seed induced the rapid formation of a stem-and-root primordium compared to the seed of P. vulgaris without B. thuringiensis /M echinosporaand NH4NO3at 100% (RC).

Figure 2 Germination of Phaseolus vulgariswith Bacillus thuringiensis and Micromonospora Echinospora with NH4NO3 reduced at 30%. Relative control (RC) = P. vulgaris without B. thuringiensis/M. echinospora fed withNH4NO3 at 100%. Treatment (T3) =P. vulgaris with B. thuringiensis/M echinospora NH4NO at 30%.

In Table 3 shows at the seedling level stage the positive response of P. vulgaris to M. echinospora with NF at 30%, which registered 42.33cm of PH and 16.16cm of RL, as well as 2.82g of AFW, 2.53g of RFW, 0.31g of ADW and 0. 11g of RDW, numerical values with statistical difference compared to phenology data: 30.83cm of PH and 14.33cm of RL; and those of biomass: 1.08g of AFW, 0.76g of RFW, 0.15g of ADW and 0.04g of RDW of P. vulgaris without B. thuringiensis and M. echinospora with NH4NO3 at 100% (RC).

Treatment/P. vulgaris*

Plant height (cm)

Root
length
(cm)

Fresh weight (g)

Dry weight (g)

Aerial

Root

Aerial

Root

Irrigated with water (AC)

18.5d**

9.16c

0.85b

0.43c

0.08dc

0.02d

+ NH4NO3at 100% (RC)

30.83c

14.33b

1.08b

0.76b

0.15bb

0.04c

B. thuringiensis +NH4NO3at 30%

36.5b

16.16a

2.69a

2.26a

0.22ab

0.08b

M. echinospora + NH4NO3 at30%

42.33a

16.16a

2.82a

2.35a

0.31aa

0.11a

B. thuringiensis/M. echinospora +NH4NO3at 30%

37.33a

15.66a

2.13a

2.05a

0.25aa

0.11a

Table 3 Growth of Phaseolus vulgaris to Bacillus thuringiensis and Micromonospora echinospora at seedling levelwith NH4NO3 reduced at30%

*n=6, ** Different letters indicate statistical difference by ANOVA/Tukey (P>0.05).

In Figure 3 shows the growth of P. vulgaris withB. thuringiensis and M. echinosporaand NH4NO3 at 30%, with increase in stem height and agreat density of the root system, compared to P. vulgaris without B. thuringiensis and M. echinospora with t at 100% (RC), since the stem had a smaller diameter and the root system was less dense.

Figure 3 Growth of Phaseolus vulgaris withBacillus thuringiensis and/or Micromonospora echinosporaat seedling level andNH4NO3reduced at 30%. Absolute control (AC) = P. vulgaris withoutB. thuringiensis/M. echinospora irrigated with water; Relative control (RC) = P. vulgaris without B. thuringiensis/M. echinospora fed with NH4NO3 at 100% ; Treatment (T) 1= P. vulgaris withB. thuringiensis + NH4NO3 at 30%; T2= P. vulgaris withM. echinospora +NH4NO3 at 30%; T3= P. vulgaris withB. thuringiensis/M. echinospora + NH4NO3at 30%.

In Table 4 shows the response of P. vulgaris to B. thuringiensis and M. echinospora at flowering level with the NF at 30% reduced dose, which registered 71.33cm of PH and 26.33cm of RL, 5.67g of AFW, 5.64g of RFW, 1.61g of ADW and 0. 32g of RWD, numerical values with statistical difference compared to 59.9cm of PH, 15.5cm of RL, 3.54g of AFW, 0.78g of RFW, 0.32g of ADW and 0.07 g of RDW of P. vulgaris without B. thuringiensis or M. echinospora with NH4NO3 at 100% or RC.

Treatment/P. vulgaris*

Plant height (cm)

Root
length
(cm)

Fresh weight (g)

Dry weight (g)

Aerial

Root

Aerial

Root

Irrigated with water (AC)

52.0c**

12.83c

1.80d

0.40b

0.26c

0.04c

with nitrogen fertilizer at 100% (RC)

59.9bc

15.5c

3.54c

0.78b

0.32c

0.07c

B. thuringiensis + NF at 30%

62.16a

18.33b

4.90a

4.46a

0.84b

0.17b

M. echinospora + NF at30%

63.66a

24.66a

5.54a

5.36a

1.15a

0.25a

B. thuringiensis/M. echinospora + NF at 30%

71.33a

26.33a

5.67a

5.64a

1.61a

0.32a

Table 4 Growth of Phaseolus vulgaris to Bacillus thuringiensis and Micromonospora echinospora at flowering level andNH4NO3reducedat 30%

*n=6, ** Different letters indicate statistical difference by ANOVA/Tukey (P>0.05).

In Figure 4, showed P. vulgaris at flowering level with B. thuringiensis and M. echinospora with NH4NO3at 30%, recorded an increase in stem thickness, greater size and number of leaves and with abundant root area system, compared to P. vulgaris without B. thuringiensis and M. echinospora with NH4NO3 at 100% or RC which had small leaves, less stem thickness and a smaller root system.

Figure 4 Growth of Phaseolus vulgaris to Bacillus thuringiensis and Micromonospora echinospora at flowering level andNH4NO3reduced at 30%. Absolute control (AC) = P. vulgaris without B. thuringiensis/M. echinospora irrigated with water; Relative control (RC) = P. vulgaris without B. thuringiensis/M. echinosporafed with NH4NO3at 100% ; Treatment (T1)=P. vulgaris with B. thuringiensiswith NH4NO3 at 30%; T2= P. vulgaris with M. echinospora + NH4NO3at 30 %, T3= P. vulgaris with B. thuringiensis/M. echinospora +NH4NO3at 30%.

In Table 5 shows at the physiological maturity level the response of P. vulgaris to B. thuringiensis and M. echinospora with NH4NO3 reduced to 30%, where it registered 125.5cm of PH and 8.83cm of RL, as well as 8.99g of AFW, 8.35g of RFW, 3.83g of ADW and 0.33g of RDW, these numerical values had statistical difference in relation to: 91.16cm of PH, 23.33cm of RL, 4.42g of AFW, 3.34g of RFW, 1.73g of ADW and 0.05g of RDW of P. vulgaris without B. thuringiensis and M. echinospora with NH4NO3 at 100% (RC).

Treatment/P. vulgaris*

Plant height (cm)

Root
length
(cm)

Fresh weight (g)

Dry weight (g)

Aerial

Root

Aerial

Root

Irrigated with water (AC)

68.83b**

15.33c

3.35b

2.72c

0.93d

0.03d

withNH4NO3at 100% (RC)

91.16b

23.33b

4.92b

3.34c

1.73c

0.05d

B. thuringiensis +NH4NO3at 30%

98.16a

26.5a

7.55a

6.06b

2.63b

0.23b

M. echinospora + NH4NO3 at
30%

117a

27a

7.90a

7.08a

3.80a

0.28a

B. thuringiensis/M. echinospora + NH4NO3 at 30%

125.5a

28.83a

8.99a

8.35a

3.83a

0.33a

Table 5 Growth of Phaseolus vulgaris at physiological maturity level to Bacillus thuringiensis and Micromonospora echinosporaand NH4NO3reducedat 30%

*n=6, ** Different letters indicate statistical difference by ANOVA/Tukey (P>0.05).

In Figure 5 shows the growth ofP. vulgaris at physiological maturity l to B. thuringiensis and M. echinospora with NH4NO3 at 30%; where a larger stem diameter was observed along with an intense green coloration, larger spike size and increased root system, compared to P. vulgaris without B. thuringiensis and M. echinospora with NH4NO3 at 100% or relative control that had a smaller spike and less density in the root system.

Figure 5 Growth of Phaseolus vulgaris at physiological maturity level withBacillus thuringiensis and Micromonospora echinosporaandNH4NO3reduced at 30%. Absolute control (AC) = P. vulgaris without B. thuringiensis/M. echinospora irrigated with water; Relative control (RC) = P. vulgaris without B. thuringiensis/M. echinospora+ NH4NO3at 100% Treatment (T1) =P. vulgaris withB. thuringiensis + NH4NO3 30%; T2= P. vulgaris with M. echinospora + NH4NO3 30%; T3= P. vulgaris with B. thuringiensis/M. echinospora +NH4NO3at 30%.

In Table 6 shows the response of P. vulgaris in biomass and fruit yield to B. thuringiensis and M. echinospora with NH4NO3 at 30% reduced dose, which registered 7.70g of fresh fruit weightand 40g of total fruit weight with 4.0Ton/ha, these values had statistical difference in relation to the 3.15g of fresh fruit weight, 28g of total fruit weight and 2.8Ton/ha yield of P. vulgaris without B. thuringiensis and M. echinospora with NH4NO3 at 100% (RC).

Treatment/P. vulgaris*

Fresh weight
of fruit (g)

Total weight of
fruit weight (g)

Yield (Ton/ha)

Irrigated with water (AC)

1.55c**

20c

0.2d

withNH4NO3at 100% (RC)

3.15b

28b

2.8b

B. thuringiensis +NH4NO3at30%

5.48a

32b

3.2a

M. echinospora + NH4NO3 at30%

6.09a

36a

3.6a

B. thuringiensis/M. echinospora +NH4NO3 at 30%

7.70a

40a

4.0a

Table 6 Yield elements of Phaseolus vulgaris with Bacillus thuringiensis and Micromonospora echinospora andNH4NO3 reduced at 30%

*n=6, ** Different letters indicate statistical difference by ANOVA/Tukey (P>0.05).

In Figure 6 shows the beneficial effect of B. thuringiensis and M. echinospora on the pods of P. vulgaris with the NH4NO3 at 30%, where an increase in size, intense green coloration and higher number of seeds were observed compared to the pods of P. vulgaris without inoculation with B. thuringiensis and M. echinospora with the NH4NO3 at 100% or RC, which are smaller and with fewer seeds.

Figure 6 Elements of yield of Phaseolus vulgariswith Bacillus thuringiensis and Micromonospora echinosporaandNH4NO3reduced at 30%. Absolute control (AC) = P. vulgaris without B. thuringiensis/M. echinosporairrigated with water; Relative control (RC) = P. vulgaris without B. thuringiensis/M. echinospora fed with NH4NO3 at 100% Treatment (T1) =P. vulgaris with B. thuringiensis+ NH4NO3 at 30%; T2= P. vulgaris withM. echinospora + NH4NO3 at 30%; T3= P. vulgaris withB. thuringiensis/M. echinospora + NH4NO3 at 30%.

Discussion

The data presented in Table 2 support the response of P. vulgaris seed to B. thuringiensis and M. echinosporawith NH4NO3at 30%, which fast emergence time of P. vulgarisseeds which were releasing organic compounds that B. thuringiensis and M. echinospora transformed into phytohormons that accelerated the emergence of root and seedling primordium.14-1 This fact that is confirmed in Figure 2, where B. thuringiensis and M. echinospora on P. vulgaris at the fifth day, after sowing showed the largest size of stem and root primordium, compared to P. vulgaris without B. thuringiensis and M. echinosporaand NH4NO3 at 100%.

In Table 3, the numerical data of phenology and biomass of P. vulgaris with M. echinospora with NH4NO3 30% at seedling stage shows that B. thuringiensis and M. echinospora converted some organic compounds from photosynthesis into phytohormons inducing karyokinesisto increasemore density of root hairs to maximize NH4NO3 uptake at 30%.17,18 As it’s been reported by Gopalakrishnan et al.,19 with C. arietinum to Streptomyces sp at NH4NO3 level of soil. Figure 3 demostratethatM. echinospora on P. vulgarisby phytohormones enhanced stem diameter and root density of P. vulgaris compared to P. vulgaris without B. thuringiensis and M. echinospora had lower stem diameter and root density, indicated that NH4NO3 at 100% shows that was not efficiently taken up by root of P. vulgaris.

In Table 4, are show values of phenology and biomass of P. vulgaris with B. thuringiensis and M. echinospora with NH4NO3 at 30% at flowering level, suggesting that which converted photosynthesis metabolites into phytohormons for P. vulgaris to reach the highest concentration in the apical zone, to improve and rapid stem and leaf growth20,21 as is observed in Figure 4. The same way as Pérez-Fernández & Alexander,22 in C. arietinumwith B. megaterium that increased RDW by enhancing uptake of NH4NO3.

In Table 5, shows the growth of P. vulgaris in terms of the phenology and biomass at physiological maturity due to B. thuringiensis and M. echinospora with NH4NO330%, its reported that organic compounds from photosynthesis transformed into phytohormones that stimulated the generation of vegetative axillary buds that induced root elongation,22-24 in that sense the root systems were able to exploration soil to uptake and optimized NH4NO3 reduced at 30%, even that with healthy plant growth, compared to P. vulgaris without B. thuringiensis and M. echinospora fed with NH4NO3 at 100% (RC), the root system grew less as its observed in Figure 5, indicating that the recommended dose was not uptake.

In Table 6, the beneficial effect of B. thuringiensis and M. echinospora on the biomass and pod yield of P. vulgaris with the dose reduced NF to 30%, which support both PGPEB maintained the conversion of photosynthesis derived carbon compounds into phytohormones:,¿ which at higher concentration stimulated the maturation of P. vulgaris pods despite the reduction of NF by up to 30%,6,25 thus P. vulgaris had healthy growth by enhancing root system formation in the soil for maximum absorption and optimization of the NF applied at 30%.26-28 The above is confirmed by what is shown in Figure 6, where the positive effect of B. thuringiensis and M. echinospora on P. vulgaris pods compared to those of RC is observed.

Conclusion

It was demonstrated that B. thuringiensis and M. echinospora, however being different genus and species endophytic bacteria are to improve germination and colonize the interior of the roots of ¨P. vulgaris; to increased root uptake of the reduced NF by up to 30%, without compromising the healthy growth of P. vulgaris. In that sense B. thuringiensis and M. echinospora endophytes of wild plants of the L. leucocephala and M. sativa types are an option for sustainable production of P. vulgaris preventing soil lost productivity and pollution due to hyper fertilization.

Author Contributions

Conceptualization JMSY and AVM; data curation, JMSY, JLIC and AVM; writing—original draft preparation, JMSY and JLIC; writing—review and editing, JMSY and JLIC; Final version JMSY. All authors have read and agreed to the published version of the manuscript.

Acknowledgments

To Project 2.7 (2022) of the Scientific Coordination of the Universidad Michoacana de San Nicolas de Hidalgo, Morelia, Mich, México. To Phytonutrimentos de Méxicoand BIONUTRA S. A. de C.V., Maravatío, Michoacán, Mexico

Conflicts of interest

The authors declared no have conflict interest for the study.

References

  1. Zahid M, Abbasi MK, Hameed S, Rahim N. Isolation and identification of indigenous plant growth promoting rhizobacteria from Himalayan region of Kashmir and their effect on improving growth and nutrient contents of maize (Zea mays L.). Frontiers in Microbiology. 2015;6:207.
  2. Cuellas MV. Horticultura periurbana, análisis de la fertilidad de los suelos en invernaderos. Chilean Journal of Agricultural & Animal Sciences. 2017;33(2):163-173.
  3. Galindo LAG, Rivas AC, Melendez JP, Mayorquín N. Alternativas microbiológicas para la remediación de suelos y aguas contaminados con fertilizantes nitrogenados. Scientia et Technica. 2020;25(1): 172-183.
  4. Cabrera EVR, Bonilla B, Aguilar M. Interacciones entre plantas y bacterias promotoras de crecimiento vegetal. Revista Citecsa. 2018;10(15):23.
  5. Moreno Reséndez A, Carda Mendoza V, Reyes Carrillo JL, Vásquez Arroyo J, Cano Ríos P. Rizobacterias promotoras del crecimiento vegetal: una alternativa de biofertilización para la agricultura sustentable. Revista Colombiana de Biotecnología. 2018;20(1):68-83.
  6. Singh M, Singh PP, Patel AK, Singh PK, Pandey KD. Enumeration of Culturable Endophytic Bacterial Population of Different Lycopersicum esculentum L. Varieties. International Journal Currrent Microbiology App Sci. 2018b;7(2):3344-3352.
  7. Azizoglu U. Bacillus thuringiensis as a biofertilizer and biostimulator: a mini-review of the little-known plant growth-promoting properties of Bt. Current Microbiology. Frontiers in Microbiology. 2019;1-7.
  8. Pérez-Fernández M, Alexander V. Enhanced plant performance in Cicer arietinum L. due to the addition of a combination of plant growth-promoting bacteria. Agriculture. 2017;7(5):40.
  9. AbdElgawad H, Abuelsoud W, Madany MM, Selim S, Zinta G, Mousa AS, Hozzein WN. Actinomycetes enrich soil rhizosphere and improve seed quality as well as productivity of legumes by boosting nitrogen availability and metabolism. Biomolecules. 2020;10(12):1675.
  10. Official Mexican standard NOM-021-SEMARNAT-2000, which establishes the specifications for fertility, salinity and soil classification, study, sampling and analysis. Mexico. DOF Secretary of the Interior. 2013.
  11. Sánchez-Yáñez JM. Brief Treatise on Agricultural Microbiology, theory and practice, Ed. Chemical Biological Research Institute. Michoacán University of San Nicolás de Hidalgo. Sustainable Research Corporation, SA de CV, Research and Development Center of the State of Michoacán, SEDAGRO. Morelia, Michoacan, Mexico. 2007.
  12. García-González MM, Farías-Rodríguez R, Peña-Cabriales JJ, Sánchez-Yáñez JM. Inoculación del trigo var. Pavón con Azospirillum spp y Azotobacter beijerinckii. Terra Latinoamericana. 2005;23(1):65-72.
  13. Walpole ER, Myers R, Myers LS. Probability & Statistics for Engineering & Science. Ed. Pearson, 8ª, 2007.
  14. González H, Fuentes N. Mechanism of action of five plan growth promoters microorganism. Revista de Ciencias Agrícolas. 2017;34(1):17-31.
  15. Jouzani GS, Valijanian E, Sharafi R. Bacillus thuringiensis: a successful insecticide with new environmental features and tidings. Applied microbiology and biotechnology. 2017;101(7):2691-2711.
  16. Rojas-Solís D, Contreras-Pérez M, Santoyo G. Mecanismos de estimulación del crecimiento vegetal en bacterias del género BacillusBiológicas. 2013;15(2):36-41.
  17. Trujillo ME, Riesco R, Benito P, Carro L. Endophytic actinobacteria and the interaction of Micromonospora and nitrogen fixing plants. Frontiers in Microbiology. 2015;6:1341.
  18. Singh DP, Patil HJ, Prabha R, Yandigeri MS, Prasad SR. Actinomycetes as potential plant growth-promoting microbial communities. In Crop Improvement Through Microbial Biotechnology. 2018ª;27-38.
  19. Gopalakrishnan S, Srinivas V, Alekhya G, Prakash B. Effect of Streptomyces sp. on growth promotion and grain yield in chickpea (Cicer arietinum L).Biotech Magazine. 2015;5(5):799-806.
  20. Tejera-Hernández B, Rojas-Badía MM, Heydrich-Pérez M. Potencialidades del género Bacillus en la promoción del crecimiento vegetal y el control biológico de hongos fitopatógenos. Revista Ciencias Químicas Ciencias Biológicas. 2011;42(3):131-138.
  21. Reyna BA, Ayala ÁT, del Carmen Barrera P. Caracterización de endófitos simbióticos aislados de leguminosas nativas de la Amazonía peruana. Ciencia Amazónica (Iquitos). 2016;6(2):150-161.
  22. Pérez-Fernández M, Alexander V. Enhanced plant performance in Cicer arietinum L. due to the addition of a combination of plant growth-promoting bacteria. Agriculture. 2017;7(5):40.
  23. Zúñiga-Sánchez E, Martínez-Barajas E, Zavaleta-Mejía E, Gamboa-de-Buen A. El floema y la ruta simplástica durante la formación de órganos de demanda. Revista Fitotecnia Mexicana. 2017;40(3):249-259.
  24. Delfim J, Dijoo ZK. Bacillus thuringiensis as a Biofertilizer and Plant Growth Promoter. In Microbiota and Biofertilizers. 2021;2(2):251-265.
  25. Gangwar M, Kaur N, Saini P, Kalia A. The diversity, plant growth promoting and anti-microbial activities of endophytic actinomycetes isolated from Emblica officinalis Gaertn. Journal of Advanced Research. 2015;3(4):1062-1071.
  26. Noumavo PA, Agbodjato NA, Baba-Moussa F, Adjanohoun A, Baba-Moussa L. Plant growth promoting rhizobacteria: Beneficial effects for healthy and sustainable agriculture. African Journal of Biotechnology. 2016;15(27):14521463.
  27. Bisht TS, Rawat L, Chakraborty B, Yadav VA. Recent advances in use of plant growth regulators (PGRs) in fruit crops. A Review. International Journal of Current Microbiology. 2018;7(05):1307–36.
  28. Wahyudi AT, Priyanto JA, Afrista R, Kurniati D, Astuti RI, Akhdiya A. Plant growth promoting activity of actinomycetes isolated from soybean rhizosphere. Journal of Biological Sciences. 2019;19:1-8.
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