Crimson Publishers Publish With Us Reprints e-Books Video articles

Full Text

Progress in Petrochemical Science

A Comprehensive Review on Biofertilizers: Mechanisms, Applications, and Challenges

Ehime Itamah*, Tajudeen Kolawole Bello, Saidu Muhammed Waziri and Sergius Ugwueke

Department of Chemical Engineering, Ahmadu Bello University, Nigeria

*Corresponding author:Ehime Itamah, Department of Chemical Engineering, Ahmadu Bello University, Zaria, Nigeria

Submission: March 18, 2025;Published: April 24, 2025

DOI: 10.31031/PPS.2025.07.000655

ISSN 2637-8035
Volume7 Issue 1

Abstract

Biofertilizers have emerged as a sustainable solution to soil degradation and declining agricultural productivity by enhancing soil fertility and nutrient availability through natural biological processes. Derived from diverse organisms such as bacteria, algae, fungi, and higher plants, biofertilizers facilitate key mechanisms like nitrogen fixation, phosphorus solubilization, and the production of growth-promoting substances. Unlike synthetic fertilizers, they prevent heavy metal accumulation, reduce environmental pollution, and mitigate climate change impacts while promoting long-term soil health. This review explores the potential of biofertilizers as eco-friendly alternatives, highlighting their role in sustainable agriculture and advocating for broader adoption to improve crop yields and environmental resilience.

Keywords:Biofertilizers; Crop yields; Pollution; Climate; Soil degradation

Introduction

Soil degradation, deforestation, and climate change pose significant threats to global food security and ecosystem stability. Land accounts for approximately 29% of Earth’s surface, with 32.7% designated for agriculture and 27% covered by forests. However, agricultural productivity is declining due to intensive farming, excessive chemical fertilizer use, and unsustainable land management practices [1]. Meanwhile, forest degradation caused by deforestation, wildfires, and resource exploitation further exacerbates environmental challenges. The overuse of nitrogen and phosphorus fertilizers has led to soil nutrient depletion, water pollution, and Greenhouse Gas (GHG) emissions [2]. Agriculture alone contributes 55% of total GHG emissions, with methane emissions from rice cultivation reaching 7.66 million metric tons annually. Additionally, nutrient runoff has resulted in widespread eutrophication, depleting oxygen in aquatic ecosystems and causing biodiversity loss [3]. In response to these challenges, biofertilizers have emerged as a sustainable alternative to synthetic fertilizers. Biofertilizers are biological products containing beneficial microorganisms that enhance soil fertility, promote plant growth, and support ecosystem health by facilitating natural nutrient cycling [4]. Unlike chemical fertilizers that supply nutrients directly, biofertilizers stimulate biological processes such as nitrogen fixation, phosphorus solubilization, and organic matter decomposition, making essential nutrients more accessible to plants while improving soil microbial activity [5]. The most widely used biofertilizers include nitrogen-fixing bacteria (Rhizobium, Azospirillum, Azotobacter), phosphate-solubilizing bacteria (Pseudomonas, Bacillus), and mycorrhizal fungi (Glomus species), which form symbiotic or associative relationships with plant roots to enhance nutrient absorption and soil structure [6].

Beyond agriculture, biofertilizers play a crucial role in forestry and ecosystem restoration. They support afforestation, reforestation, and soil reclamation efforts by improving tree survival rates, accelerating nutrient cycling, and enhancing soil rehabilitation in degraded landscapes. Their application in forestry has proven effective in increasing biomass production, restoring biodiversity, and mitigating climate change through enhanced carbon sequestration [7]. Despite their numerous benefits, the large-scale adoption of biofertilizers remains limited due to several challenges. Their effectiveness varies under different environmental conditions, they have a relatively short shelf life, and many farmers and foresters lack awareness of their advantages. Moreover, the complex interactions between biofertilizers and native soil microbial communities necessitate site-specific application strategies tailored to different agroecological zones. Addressing these challenges requires advancements in formulation technology, improved regulatory frameworks, and widespread education on their benefits [8]. This review provides a comprehensive analysis of the science and practical applications of biofertilizers. It explores the different types of biofertilizers, their mechanisms of action, and their impact on soil health and plant productivity. Furthermore, it examines their role in both traditional and modern agricultural systems, their importance in sustainable forestry, and the challenges associated with their application [9]. By synthesizing recent scientific advancements and field studies, this review highlights the current state of biofertilizer technology, identifies future research directions, and underscores their potential in promoting food security while preserving environmental integrity [9].

Biofertilizers: A Sustainable Alternative for Agriculture

Ensuring sufficient food production for the world’s growing population while maintaining ecological balance is one of the biggest challenges of the 21st century. Sustainable agriculture has become a global priority, emphasizing not only increased crop yields but also environmental conservation [10]. Over-reliance on chemical fertilizers has led to severe consequences, including soil degradation, water contamination, and disruption of nutrient cycles. Excessive application of synthetic fertilizers reduces soil fertility, alters its water retention capacity, and creates an imbalance in essential nutrients. Furthermore, plants grown with chemical fertilizers and pesticides can accumulate harmful substances, which may pose health risks to humans [11]. The production of chemical fertilizers releases toxic gases such as Ammonia (NH₄), Carbon Dioxide (CO₂), and Methane (CH₄), contributing to air pollution and climate change. Additionally, industrial waste from fertilizer manufacturing is often discharged into water bodies, causing severe contamination [12]. One of the most damaging outcomes is water eutrophication, where excess nutrients promote algal blooms that deplete oxygen levels, leading to aquatic biodiversity loss. Longterm use of synthetic fertilizers also contaminates the soil, reducing its quality and sustainability [13]. Only about half of the nitrogen applied through chemical fertilizers is utilized by crops, while the remainder is lost through volatilization, runoff, or interactions with organic compounds in the soil. Nitrates, a key component of fertilizers, often seep into groundwater and surface water sources, posing serious health risks [14]. High concentrations of nitrates, nitrites, and nitrosamines are linked to conditions such as blue baby syndrome (methemoglobinemia in infants), gastric cancer, goiter, congenital disabilities, heart disease, and further eutrophication of water bodies. The excessive use of chemical fertilizers also contributes to Greenhouse Gas (GHG) emissions, weakening the protective ozone layer and exposing humans to harmful ultraviolet radiation. Agricultural soils account for 60% of human-induced Nitrous Oxide (N₂O) emissions, a greenhouse gas that has 310 times the global warming potential of carbon dioxide [8]. Uncontrolled nitrogen fertilizer application releases Nitrogen Oxides (NO, N₂O, NO₂) into the atmosphere, significantly worsening air pollution. The accumulation of heavy metals such as arsenic and cadmium from chemical fertilizers further threatens human health. If these unsustainable practices continue, long-term soil degradation and loss of beneficial microorganisms could severely impact global food security. To transition toward sustainable agriculture, it is essential to adopt nutrient management practices that are both cost-effective and environmentally friendly. One promising alternative is the use of biofertilizers [9].

Biofertilizers: A Natural Solution for Soil and Crop Health

Biofertilizers, also known as microbial inoculants, are formulations containing living microorganisms that colonize plant roots and enhance nutrient availability. These beneficial microbes fix atmospheric nitrogen, solubilize phosphorus, and synthesize plant growth-promoting compounds, improving plant health and productivity [15]. Unlike chemical fertilizers, which provide direct nutrient input, biofertilizers work by stimulating biological processes that sustain soil fertility over the long term. By reducing the need for synthetic fertilizers and pesticides, biofertilizers contribute to a healthier and more balanced agricultural ecosystem [16]. Some microbial strains not only facilitate nutrient absorption but also produce essential vitamins and phytohormones that enhance plant growth and resistance to environmental stress [17]. Biofertilizers can be classified based on their mode of action, microbial composition, and intended purpose. Their effectiveness depends on agricultural practices, soil conditions, and environmental factors [18]. Future advancements in biofertilizer technology will be key to achieving sustainable agricultural goals, particularly through biological nitrogen fixation and plant-microbe interactions. Microorganisms also play a crucial role in nutrient cycling, helping maintain ecosystem stability [19]. The microbial community within the soil enhances nutrient availability, uptake, and solubility, making essential micronutrients and macronutrients more accessible to plants [20]. Beneficial bacteria perform several key functions, including:
i. Nitrogen fixation for improved soil fertility.
ii. Phosphorus solubilization to increase plant nutrient absorption.
iii. Phytohormone production, which regulates plant growth and stress responses.
iv. Biological pest control, reducing the need for synthetic pesticides.

As research progresses, biofertilizers will play an increasingly vital role in ensuring sustainable agriculture, reducing environmental pollution, and maintaining soil health. With proper policy support, farmer education, and improved production techniques, biofertilizers can emerge as a viable, eco-friendly alternative to chemical fertilizers, contributing to global food security while preserving natural ecosystems [21] (Figure 1).

Figure 1:Summary of the Manuscript.


The Role of Biofertilizers in Enhancing Agricultural Productivity

The use of biofertilizers in agriculture has gained significant attention due to extensive research on their impact on crop growth. However, their effects on forestry species remain less explored. As agricultural and environmental challenges intensify, biofertilizers are emerging as a viable alternative to synthetic fertilizers, offering a sustainable approach to improving soil health and crop productivity [22].

Mechanisms of biofertilizer action

To fully leverage the potential of biofertilizers, it is essential to understand their modes of action, which include nutrient assimilation, phytohormone regulation, and plant protection. Biofertilizers enhance soil fertility by supplying essential nutrients such as nitrogen, phosphorus, and potassium, preserving the soil’s natural properties while reducing dependence on chemical fertilizers [23].

Plant Growth-Promoting Microorganisms (PGPMs) are classified into three main groups:

a. Arbuscular Mycorrhizal Fungi (AMF)-These fungi establish symbiotic relationships with plant roots, improving water and nutrient absorption [24].
b. Plant Growth-Promoting Rhizobacteria (PGPR)-These beneficial bacteria enhance nutrient uptake, promote root development, and provide resistance against plant pathogens [25].
c. Nitrogen-Fixing Rhizobia-These microbes convert atmospheric nitrogen into forms that plants can easily absorb, boosting plant growth and productivity [26].

Among nitrogen-fixing bacteria, Rhizobium, Azotobacter, and Azospirillum play a crucial role in making atmospheric nitrogen available for plant uptake, thereby reducing the need for synthetic nitrogen fertilizers [27]. Additionally, phosphorus-solubilizing bacteria such as Pseudomonas and Bacillus break down organic and inorganic phosphorus compounds, ensuring optimal nutrient availability for plants. Some biofertilizers, including Azotobacter and Azospirillum, secrete plant growth-promoting compounds that enhance root elongation and nutrient absorption [28]. Furthermore, biofertilizers contribute to hormone production, releasing auxins, gibberellins, and cytokinins, which regulate plant growth, promote flowering, and enhance fruit development. These bioactive compounds play a vital role in stimulating root growth, increasing biomass, and improving overall plant vigor [29]. Beyond nutrient enrichment, biofertilizers provide protection against environmental stressors. They help combat soil-borne diseases by producing antibiotics and antifungal compounds, which suppress pathogenic microbes. Additionally, they assist in reducing heavy metal toxicity by binding and neutralizing harmful metals in the soil, minimizing pollution risks. Some biofertilizers also trigger the production of phenolic compounds, which strengthen the plant’s natural defense mechanisms against pests and diseases [30].

Scientific Basis of Biofertilizers

Biofertilizers are an essential component of sustainable agriculture, leveraging the natural capabilities of beneficial microorganisms to enhance soil fertility and plant growth. Unlike chemical fertilizers, biofertilizers rely on living organisms to promote plant health and productivity [31]. Their effectiveness is rooted in well-established biological processes, including nitrogen fixation, phosphorus solubilization, and the enhancement of soil microbiomes. This section delves into the microbial composition of biofertilizers, their mechanisms of action, and their interactions with plants [32].

Microbial composition and functions

Biofertilizers consist of various beneficial microorganisms that actively contribute to soil health and plant nutrition. These microbes establish either direct or indirect interactions with plants, improving nutrient availability and promoting overall plant vigor [33].

Common microorganisms used in biofertilizers: Several key microbial groups are used in biofertilizer formulations, each playing a distinct role in enhancing soil fertility:
a. Rhizobium-A symbiotic nitrogen-fixing bacterium that forms nodules on the roots of leguminous plants. It converts atmospheric nitrogen into a plant-usable form, reducing the need for synthetic nitrogen fertilizers.
b. Azospirillum-A free-living nitrogen-fixing bacterium that associates with the roots of cereals and grasses, promoting root elongation and nutrient uptake [34].
c. Azotobacter-A non-symbiotic nitrogen-fixing bacterium that thrives in the rhizosphere, enhancing soil fertility and producing plant growth-promoting substances.
d. Mycorrhizae-A type of beneficial fungus that forms mutualistic associations with plant roots, increasing water and nutrient absorption, particularly phosphorus [35].
e. Phosphate-Solubilizing Bacteria (PSB)-Microorganisms such as Pseudomonas and Bacillus that break down insoluble phosphate compounds in the soil, making phosphorus available for plant uptake.
f. Potassium-Solubilizing Bacteria (KSB)-Microbes that help release potassium from soil minerals, improving plant growth and stress resistance [36].

Biological processes involved: Biofertilizers function by harnessing natural microbial processes that enhance nutrient availability and soil health. These include:
a. Nitrogen Fixation-The conversion of atmospheric Nitrogen (N₂) into Ammonia (NH₃) by bacteria such as Rhizobium and Azospirillum, providing plants with an essential nutrient for protein synthesis [37].
b. Phosphorus Solubilization-The transformation of insoluble phosphate compounds into bioavailable forms through the action of phosphate-solubilizing bacteria.
c. Potassium Mobilization-The release of potassium from soil particles by potassium-solubilizing bacteria, which helps plants in enzyme activation, photosynthesis, and stress tolerance [38].
d. Production of Growth-Promoting Substances-Many biofertilizer microbes produce hormones such as auxins, gibberellins, and cytokinins that stimulate root development, enhance nutrient uptake, and improve plant growth [39].
e. Biocontrol Activity-Some biofertilizers contain microbes that suppress plant pathogens by outcompeting harmful microorganisms, producing antimicrobial compounds, or inducing plant defense mechanisms [40].

By incorporating these microorganisms into agricultural practices, biofertilizers enhance soil fertility, improve plant health, and reduce dependency on chemical fertilizers.

Mode of action and interaction with plants

Biofertilizers interact with plants in various ways, either by forming symbiotic relationships or by enhancing soil microbial activity through non-symbiotic mechanisms. These interactions play a crucial role in improving nutrient uptake, soil structure, and overall plant resilience [41].

Symbiotic and non-symbiotic mechanisms:

a. Symbiotic Mechanisms-These involve a close, mutually beneficial relationship between plants and microorganisms. For example:
i. Rhizobium forms nodules on the roots of legumes, where it fixes atmospheric nitrogen in exchange for carbon from the plant.
ii. Mycorrhizal fungi penetrate plant roots, extending their hyphae into the soil to absorb phosphorus and other nutrients in return for plant-produced sugars [42].
b. Non-Symbiotic Mechanisms-Some microbes function independently in the soil but still benefit plant growth. For example:
i. Azotobacter fixes atmospheric nitrogen without forming plantroot associations.
ii. Phosphate-solubilizing bacteria release enzymes that convert inorganic phosphate into a form that plants can absorb [43].

Influence on root architecture and nutrient absorption

Biofertilizers significantly influence root development, leading to better nutrient uptake and plant growth. These effects include:
i. Enhanced Root Elongation-Certain biofertilizer bacteria, such as Azospirillum, stimulate root elongation and branching, increasing the plant’s ability to absorb water and nutrients.
ii. Increased Root Surface Area-Mycorrhizal fungi create extensive networks of hyphae that improve nutrient and water absorption, particularly in nutrient-deficient soils [44].
iii. Improved Soil Structure-The microbial activity associated with biofertilizers enhances soil aggregation and porosity, leading to better aeration and water retention [45].
iv. Stimulated Hormone Production-Microbial interactions often trigger the production of plant growth hormones like auxins, which regulate root development and overall plant growth [46].

By fostering these beneficial interactions, biofertilizers not only improve soil fertility but also contribute to more sustainable and resilient agricultural systems.

Current Trends in Biofertilizer Use in Agriculture and Forestry

With the increasing global focus on sustainable farming and integrated nutrient management, biofertilizers are gaining traction, particularly in developing countries. Governments, agricultural institutions, and environmental organizations are actively promoting biofertilizers as an alternative to chemical fertilizers to enhance soil fertility, reduce carbon footprints, and promote climate-resilient agriculture [47]. Despite the growing market demand, biofertilizer adoption remains uneven across regions, primarily due to challenges such as inconsistent efficacy, limited production scalability, short shelf life, and a lack of farmer awareness [48]. While some regions, including China, India, North America, and Europe, have made significant progress in commercial biofertilizer production, many areas still rely heavily on chemical fertilizers due to policy gaps and limited research investments.

To accelerate the transition to biofertilizer-based agriculture, there is a need for:
i. Standardized formulations to ensure consistent effectiveness across different soil types and crops.
ii. Cost-efficient production techniques to make biofertilizers more accessible to farmers.
iii. Regulatory frameworks that encourage biofertilizer innovation and market expansion.
iv. Farmer education and awareness programs to promote largescale adoption [49].

As biofertilizers continue to evolve, they hold immense potential to transform agriculture and forestry by enhancing soil health, reducing environmental pollution, and increasing crop yields sustainably. Strengthening research, policy support, and investment in biofertilizer technology will be key to achieving longterm food security and environmental conservation [50-73] (Table 1).

Table 1:Types of Biofertilizers, Their Mechanisms, and Examples.


Expanding the Use of Biofertilizers in Agriculture and Forestry

The growing global focus on sustainable agricultural and forestry practices has led to a significant rise in the adoption of biofertilizers. As concerns about environmental degradation and soil health increase, there has been a notable shift towards integrated nutrient management strategies [74,75]. This shift has brought greater attention to the benefits of biofertilizers, including Arbuscular Mycorrhizal Fungi (AMF), Phosphorus-Solubilizing Bacteria (PSB), Azospirillum, Azotobacter, Rhizobium, Acetobacter, and even seaweed-based fertilizers [76]. Countries such as China, Canada, Argentina, and several European nations, including Spain, Italy, and Germany, are actively promoting biofertilizer use due to the increasing demand for organic farming and eco-friendly agricultural solutions [77]. Similarly, in the United States, India, and Africa, the awareness of biofertilizers’ role in enhancing soil fertility and crop productivity has grown substantially. The expansion of organic farming worldwide is evident, with the total agricultural land under organic cultivation rising from 69.4 million hectares in 2017 to 74.9 million hectares in 2020. This increase is driven by a greater consumer preference for organic products and sustainable farming techniques [78,79].

Biofertilizers play a crucial role in enhancing soil fertility by acting as seed or soil inoculants, promoting plant growth, and actively participating in the nutrient cycle. Their widespread use in agriculture and forestry is attributed to their ability to replace chemical fertilizers while being cost-effective, environmentally friendly, and capable of improving soil structure and productivity by 10-25% without causing harm to ecosystems [80,81]. In addition to boosting yields, biofertilizers contribute to soil conservation by reducing erosion and enhancing water retention, making them a valuable alternative for long-term agricultural sustainability. Recent research has focused on maximizing the efficiency of biofertilizers by addressing issues such as soil salinization, heavy metal contamination through phytoremediation, and increasing plant resilience to extreme environmental conditions [82,83]. Some of these studies have advanced from laboratory experiments to field trials, demonstrating the potential for large-scale application. Scientists are continuously working on improving biofertilizer technology to reduce production costs, maintain quality, and increase farmer adoption rates [84]. Innovative approaches such as nanotechnology are revolutionizing biofertilizer development. Nano-fertilizers, nano-biofertilizers, and nano-pesticides are emerging as advanced, low-cost, and environmentally friendly alternatives to traditional fertilizers. Additionally [85], highthroughput sequencing is being explored to restore agricultural microbiomes that have been disrupted by unsustainable farming practices. This approach aims to identify and reintroduce beneficial microbes involved in essential soil processes, particularly those related to phosphorus cycling, to create more resilient and productive agricultural systems [86-88] (Figure 2 & 3).

Figure 2:Mechanism of Action Involves in Biofertilizer [85].


Figure 3:Block Diagram Visually Represents How Biofertilizer Inoculation Affects Soil Physicochemical and Biochemical Properties [86].


The Role of Biofertilizers in Forestry and Their Ecological Benefits

Biofertilizers play a crucial role in forest ecosystems by enhancing soil fertility, promoting plant growth, and improving resilience to environmental stress. They are an essential component of integrated nutrient management strategies, incorporating nitrogen-fixing bacteria, potassium and phosphorus solubilizers, Plant Growth-Promoting Rhizobacteria (PGPR), ectoand endomycorrhizal fungi, cyanobacteria, and other beneficial microorganisms [89]. These biofertilizers contribute significantly to nutrient and water absorption, helping trees withstand both biotic and abiotic stressors [90,91]. Ectomycorrhizal fungi (ECMF) are particularly vital in forest ecosystems, forming a symbiotic relationship with tree roots through specialized structures such as the Hartig net [92]. This association aids in nutrient cycling, improves soil stability, and contributes to forest restoration efforts. ECMF have proven effective in rehabilitating degraded lands, including sites affected by heavy metal contamination, soil erosion, and wildfires. They also assist in establishing tree plantations by reducing reliance on chemical fertilizers and fostering sustainable forestry practices [93]. With over 7,000 species, ECMF are widely associated with commercially valuable trees such as poplar, birch, oak, pine, and spruce. These fungi facilitate nutrient and water exchange between soil and trees in return for carbon from the plant. ECMF applications have been instrumental in restoring lands damaged by industrial activities, including mining and deforestation [94]. For instance, certain ECMF species, such as Pisolithus albus, have been successfully used to rehabilitate forests affected by mining activities by enhancing tree growth and protecting plants from toxic metal accumulation. ECMF also play a role in restoring forests affected by clear-cut logging [95]. Studies indicate that transferring soil from mature forests to these sites encourages the formation of beneficial microbial communities, improving soil health and aiding tree establishment. Additionally, some ECMF species have demonstrated resilience to wildfires, capturing and transferring nitrogen to surviving vegetation, thus stabilizing the ecosystem post-fire. This makes them valuable tools for reforestation and habitat restoration in fire-prone regions [96].

The invasion of non-native species, such as pine trees in the Southern Hemisphere, has disrupted native forest ecosystems. These invasions are often facilitated by the presence of invasive ECMF species, which outcompete native microbial communities [97]. To counteract this, researchers are exploring the use of non-invasive ECMF strains as biofertilizer inoculants for reforestation efforts, helping maintain ecological balance while still supporting forestry industries [98]. Plant growth is also influenced by microbial communities in the rhizosphere, where PGPRs enhance nutrient availability and promote plant health. These bacteria contribute to processes such as nitrogen fixation, phosphate solubilization, and phytohormone production, which aid in tree growth and stress tolerance [99]. In semi-arid regions, biofertilizers like biochar and PGPRs have been effective in mitigating water stress in tree seedlings, facilitating afforestation efforts in challenging environments. Certain bacterial strains, such as Brevibacillus reuszeri MPT17, have been found to enhance root development and nutrient uptake in tree species like pecan (Carya illinoinensis), while others, including Bacillus paramycoides and Schizophyllum commune, have demonstrated the ability to help trees survive in saline conditions [100]. Cyanobacteria also play a significant role in forest ecosystems, particularly in nitrogen cycling. These microorganisms contribute substantial amounts of nitrogen to boreal forests, forming associations with feather mosses such as Hylocomium splendens and Pleurozium schreberi [101]. By enhancing nitrogen availability in forest soils, cyanobacteria promote tree growth and support overall ecosystem health. Biofertilizer applications in forestry have been linked to improved tree growth, increased yields, and enhanced wood quality [102]. Different biofertilizers exhibit specific benefits; for instance, Azotobacter is highly effective in increasing soil organic matter and nitrogen levels, while Phosphorus-Solubilizing Bacteria (PSB) improve phosphorus and potassium availability, leading to better seedling development [103]. Studies have identified promising microbial isolates, including Lysinibacillus sphaericus, Paenibacillus quercus, Paramyrothecium roridum, and Lysinibacillus fusiformis, which have shown significant potential in enhancing the growth of tree species such as Eucalyptus pellita. Further research is needed to refine these biofertilization techniques and optimize their application in sustainable forestry practices [104]. Forests harbor diverse microbial communities, many of which remain unexplored. Understanding these microbial interactions is essential for harnessing their full potential in forest management and conservation efforts. As research advances, biofertilizers will continue to play an integral role in promoting healthy forest ecosystems and supporting sustainable afforestation projects worldwide [105].

Challenges in the Application of Biofertilizers

Biofertilizers offer an environmentally sustainable, costeffective, and renewable alternative to chemical fertilizers. However, their widespread adoption faces several obstacles that impact their production, market viability, and practical usage [106]. These challenges include slow action, formulation complexities, sensitivity to environmental conditions such as temperature and moisture, lack of specific microbial strains, inadequate manufacturing facilities, shortage of skilled labor, seasonal demand due to microbial activity, regulatory hurdles, and limited market awareness [107]. The effectiveness of biofertilizers, as seen in various microbial applications, depends on the development of specialized microbial strains, optimized formulations, and reliable field-testing methodologies [108].

Complexity in biofertilizer formulation

The growing interest in biofertilizers has led to the availability of various products worldwide. However, the formulation process plays a crucial role in determining the quality and effectiveness of these biological agents. Preparing biofertilizer inoculants involves multiple steps, including selecting appropriate microbial strains, using suitable carriers, and incorporating additives that support microbial survival during storage, transportation, and soil application [109]. A well-formulated biofertilizer ensures the efficient introduction of beneficial microbes into the target environment, enhancing their functionality upon application. Additionally, affordability remains a key consideration in formulation, requiring the use of cost-effective carriers and organic materials [110]. One of the primary challenges in biofertilizer formulation is the discrepancy between laboratory success and field performance. While some microbial strains show promising results in controlled environments, their effectiveness in realworld conditions can be unpredictable [111]. Manufacturers often combine multiple microbial strains, such as Rhizobia with Arbuscular Mycorrhizal Fungi (AMF) or Phosphate-Solubilizing Bacteria (PSB), to maximize benefits for plants. The physical nature of the carrier material also affects biofertilizer formulation, leading to four major types: solid carrier-based, liquid-based, polymerentrapped, and pressurized dry formulations [112].

Liquid formulations, while easy to apply, often suffer from rapid declines in microbial activity after production. Solid formulations, on the other hand, pose challenges for non-sporulating bacteria, as desiccation can damage cell membranes, leading to microbial death and reduced viability during rehydration [113]. This limitation hinders large-scale commercialization. Although immobilized-cell formulations improve microbial stability, they remain expensive due to the high cost of polymeric carriers, making large-scale production and field application difficult. Additionally, cell mortality is a significant challenge in bio-encapsulation, particularly during drying processes, as limited oxygen transfer affects microbial survival [114]. Another issue with certain formulations, such as fluidized-bed dry formulations, is their short shelf life and susceptibility to contamination due to moisture content in carrier-based inoculants [115]. Contamination by unwanted microorganisms can alter the biofertilizer’s effectiveness, making it essential to maintain sterile production conditions. However, ensuring sterility adds to production costs, making the final product less affordable for farmers [116]. To increase the adoption of biofertilizers, there is a pressing need to develop formulations that are more stable, cost-effective, and tailored to meet agricultural and forestry needs. Advancements in formulation technology should focus on improving microbial survival rates, extending shelf life, enhancing field performance, and maintaining affordability. Addressing these challenges will help maximize the potential of biofertilizers in sustainable forestry and agriculture [117].

Environmental and Storage Challenges in Biofertilizer Application

Impact of climatic conditions on efficacy

The effectiveness of biofertilizers is significantly influenced by environmental conditions, as microbial inoculants are exposed to various biotic and abiotic stress factors upon soil application [118]. These stressors include competition with native microflora and microfauna, as well as environmental conditions such as soil pH, temperature fluctuations, and salinity. In semi-arid regions, harsh climatic factors such as drought, high salinity, inadequate irrigation, and soil erosion make it difficult for introduced microbial strains to establish and survive. These conditions rapidly deplete beneficial bacteria, reducing the long-term effectiveness of biofertilizers [119]. Microbial strains also face challenges during storage, particularly in peat-based carriers, where temperature fluctuations can affect their viability. Many Gram-negative bacterial strains, which are commonly used in biocontrol and plant growth promotion, exhibit poor tolerance to extreme temperatures and drought [120]. This sensitivity complicates the development of stable bioformulations. For instance, Phosphate-Solubilizing Bacteria (PSB) used in forestry applications must be adapted to withstand cold temperatures if they are to function effectively in subfreezing environments [121]. While psychrotolerant PSB species can remain active in such conditions, their efficiency at room temperature also makes them versatile biofertilizers for a range of environmental conditions. Plant Growth-Promoting Bacteria (PGPB) present additional challenges due to their inconsistent behavior in the field. Their effectiveness varies depending on plant species, environmental conditions, and interactions with native microbial communities [122-124]. Furthermore, large-scale production of certain PGPB strains is difficult, as they often struggle to grow as efficiently in controlled culture systems as they do in their natural habitat. Given the rapidly changing global climate, biofertilizer formulations must be adapted to region-specific conditions to ensure long-term efficacy and sustainability [125,126].

Storage challenges and shelf life

Storage conditions play a crucial role in maintaining the viability and effectiveness of biofertilizers. Factors such as temperature, humidity, and exposure to sunlight significantly impact microbial survival, the quality of carrier materials, and overall product stability. For biofertilizers to remain effective, they must retain a sufficient number of viable microbial cells throughout storage [127]. However, a major challenge is the limited shelf life of live microbial inoculants, which typically lasts between 4 to 6 months when stored at temperatures ranging from 20°C to 25°C. Additional care during storage and transportation is required to prevent microbial degradation, increasing overall production and distribution costs [128]. To maintain biofertilizer potency, proper storage conditions are essential. The recommended storage temperature for extended shelf life is around 4°C, as lower temperatures help preserve microbial viability. For instance, Azotobacter venelandi has been found to retain its viability for up to 90 days at 5°C, while Acinetobacter baumannii remains effective for over six months, exceeding the minimum required viable cell count. However, certain bacterial strains, such as Burkholderia species, show better survival at 28°C, highlighting the importance of strainspecific storage conditions [129]. Before application, biofertilizers stored at 4°C should be acclimated by culturing them at 26°C for at least seven days to allow microbial multiplication and ensure the required cell count is achieved [130]. Proper storage not only ensures biofertilizer effectiveness but also impacts accessibility, as inadequate storage facilities limit product availability in rural areas. Addressing these challenges by improving storage technology, developing more resilient microbial strains, and optimizing formulations for diverse climatic conditions will be essential for the broader adoption of biofertilizers in sustainable agriculture [131].

Enhancing the Efficacy, Storage, Application, and Market Growth of Biofertilizers

Impact of climatic conditions on biofertilizer effectiveness

Biofertilizer technology is highly influenced by environmental factors, which can impact its efficacy. The microorganisms in biofertilizers are subject to biotic stress from microflora and microfauna, as well as abiotic stress from soil pH, temperature variations, and salinity. In semi-arid regions, introduced microbial inoculants struggle to survive due to extreme conditions such as drought, high salinity, insufficient irrigation, and soil erosion, which deplete the microbial population quickly [132]. Temperature fluctuations further affect the viability of bacteria, particularly during storage in peat-based carriers. Many beneficial bacterial strains, especially Gram-negative biocontrol bacteria, are highly sensitive to environmental changes, making bioformulation challenging [133]. For example, Phosphorus-Solubilizing Bacteria (PSB) adapted to cold climates are required to function efficiently in subfreezing temperatures, whereas psychrotolerant PSB species that thrive at room temperature are suitable for general applications. However, the effectiveness of Plant Growth-Promoting Bacteria (PGPB) remains inconsistent across different plant species and environmental conditions, often leading to unreliable productivity. Additionally, large-scale production is challenging as many PGPB strains exhibit slow growth in artificial culture conditions compared to their natural habitat. Future strategies should consider region-specific climatic forecasts to enhance biofertilizer performance under changing global conditions [134].

Optimizing storage conditions for biofertilizers

Proper storage conditions significantly impact microbial survival, product longevity, and field efficacy. Key storage factors include temperature, humidity, and exposure to sunlight. The carrier material should ensure the long-term viability of microorganisms and maintain a sufficient number of live cells throughout the storage period [135]. One of the primary challenges with biofertilizers is their limited shelf life, typically around 4-6 months at 20-25°C [136]. Storing them at 4°C significantly extends their viability, with some bacterial strains such as Acinetobacter baumannii maintaining required cell counts beyond six months. Conversely, Burkholderia species show better viability when stored at 28°C for up to two months, highlighting the need for strainspecific storage guidelines [137]. When refrigerated biofertilizers are used, they should be incubated at 26°C for at least seven days before application to reactivate microbial multiplication. Limited access to adequate storage facilities in rural areas often hinders product availability and adoption, making decentralized cold storage solutions a necessary investment for wider implementation [138].

Practical Applications in Agriculture and Forestry

Biofertilizers play a vital role in sustainable agricultural and forestry practices, offering an eco-friendly alternative to synthetic fertilizers. Their application enhances soil fertility, promotes plant growth, and aids in environmental conservation [139]. Biofertilizers can be applied through various methods, including seed inoculation, root dipping, and direct soil application in dry or liquid form. In seed inoculation, biofertilizers are mixed into a slurry and evenly coated onto sterile seeds before drying and planting [140]. The root-dipping technique is primarily used for transplanted crops, where plant roots are submerged in a biofertilizer solution before transplantation. Alternatively, biofertilizers can be applied as a foliar spray or soil treatment at the appropriate planting stage [141]. Despite their benefits, several obstacles hinder widespread adoption. Biofertilizers often perform inconsistently in the field compared to controlled environments due to variable climate, soil composition, crop type, and biodiversity. They also require more time to colonize roots and enhance plant growth compared to synthetic fertilizers, which deliver immediate results [142]. Challenges include limited awareness among farmers about the ecological advantages of microbial biofertilizers, inadequate promotion by agricultural extension services, lack of suitable carrier materials for formulation, and insufficient storage infrastructure. Moreover, inadequate labeling regarding expiration dates and microbial composition raises doubts about product authenticity [143], further affecting acceptance among farmers. This section explores the practical use of biofertilizers in sustainable agriculture, forestry, and ecosystem restoration, along with the most effective field application methods [144].

Use in sustainable agriculture

The adoption of biofertilizers in sustainable agriculture is increasing due to their ability to improve crop productivity while minimizing environmental impact. By enhancing soil health and reducing dependence on chemical fertilizers, biofertilizers contribute to organic farming and sustainable crop production systems [145].

Organic farming practices

Biofertilizers are widely used in organic farming, where chemical fertilizers and pesticides are restricted. Their role in organic agriculture includes:
i. Improving soil fertility-Biofertilizers enhance nutrient cycling, maintaining long-term soil productivity without depleting natural resources.
ii. Reducing chemical inputs -The use of biofertilizers minimizes synthetic fertilizer application, reducing soil and water contamination.
iii. Enhancing plant health-Many biofertilizers contain microbes that suppress plant pathogens and improve crop resistance to diseases.
iv. Supporting biodiversity-The introduction of beneficial microbes into the soil improves microbial diversity, fostering a balanced ecosystem [1,146].

Crop-specific applications

Different crops benefit from specific biofertilizers based on their nutrient requirements and growth conditions. Some key applications include:
i. Cereals (Rice, Wheat, Maize, etc.)-Azospirillum and Azotobacter are commonly used to enhance nitrogen fixation and promote root growth. Phosphate-solubilizing bacteria improve phosphorus uptake, leading to higher yields [147].
ii. Legumes (Soybean, Peas, Lentils, etc.)-Rhizobium is essential for nitrogen fixation in leguminous plants, improving their growth and reducing the need for nitrogen fertilizers.
iii. Vegetables (Tomatoes, Carrots, Spinach, etc.)-Mycorrhizal fungi and potassium-solubilizing bacteria enhance nutrient absorption, leading to improved quality and productivity [148].

The targeted use of biofertilizers in different cropping systems ensures maximum efficiency, leading to sustainable and profitable agricultural production.

Role in forestry and ecosystem restoration

Biofertilizers are increasingly recognized for their role in forestry and ecosystem restoration, where they help in soil improvement, afforestation, and the rehabilitation of degraded lands.

Benefits in afforestation and soil reclamation

i. Enhancing Tree Growth-Mycorrhizal fungi significantly improve nutrient uptake in forest tree species, leading to better establishment and growth in degraded lands.
ii. Improving Soil Structure-The use of biofertilizers increases soil aggregation, organic matter content, and microbial activity, making soils more fertile and resilient [149,150].
iii. Rehabilitating Degraded Lands-In areas affected by deforestation, mining, and erosion, biofertilizers accelerate soil recovery and support the re-establishment of native plant species.
iv. Enhancing Carbon Sequestration-Biofertilizers contribute to carbon sequestration by increasing plant biomass and promoting soil organic matter accumulation, helping mitigate climate change [151].

Case studies on forest tree growth

Several studies demonstrate the effectiveness of biofertilizers in forestry:
a. Case Study 1: Mycorrhizal Inoculation in Pine and Eucalyptus Plantations
i. Forest nurseries inoculated with mycorrhizal fungi showed a significant increase in seedling survival rates and biomass production.
b. Case Study 2: Rhizobium Application in Acacia and Albizia Species
i. Nitrogen-fixing bacteria improved tree growth and soil nitrogen levels in reforestation projects, reducing the need for chemical fertilizers.
c. Case Study 3: Phosphate-Solubilizing Bacteria in Mangrove Restoration
i. The introduction of phosphate-solubilizing microbes enhanced root development and nutrient uptake, improving mangrove establishment in degraded coastal zones [152].

These examples highlight how biofertilizers can be integrated into forestry projects to enhance sustainability and ecosystem recovery.

Field application methods

The effectiveness of biofertilizers depends on their proper application. Various methods can be used to ensure optimal plantmicrobe interactions and maximize benefits.

Seed treatment

a. Biofertilizers are applied as a coating on seeds before planting to enhance early root colonization.
b. Commonly used for legumes with Rhizobium and cereals with Azospirillum.
c. Improves seed germination, root development, and nutrient uptake.
d. Application Method:
i. Mix biofertilizer powder or liquid with a sticking agent (e.g., sugar solution) before applying to seeds.
ii. Allow seeds to dry in shade before sowing [153,154].

Soil inoculation

a. Direct application of biofertilizers to soil improves microbial populations and nutrient availability.
b. Suitable for phosphate-solubilizing bacteria, potassiummobilizing bacteria, and mycorrhizal fungi.
c. Enhances soil structure, organic matter content, and nutrient cycling.
d. Application Method:
i. Mix biofertilizer with compost or organic manure before applying to soil.
ii. Apply around the root zone to ensure effective colonization [155,156].

Foliar application

a. Some biofertilizers can be applied as a liquid spray on plant leaves to enhance nutrient uptake and stress resistance.
b. Particularly useful for microbial bio-stimulants that produce plant growth hormones.
c. Application Method:
i. Dilute biofertilizer solution as per recommended concentration.
ii. Spray evenly on foliage during the early morning or late afternoon to maximize absorption [157].

Best practices and dosage recommendations

To maximize the benefits of biofertilizers, the following best practices should be followed:
a. Use Fresh and Viable Biofertilizers-Ensure biofertilizers are stored under appropriate conditions and used before their expiry date.
b. Apply Under Favorable Conditions-Optimal soil moisture, temperature, and pH levels enhance microbial activity [158].
c. Combine with Organic Matter-Adding compost or farmyard manure improves microbial survival and effectiveness.
d. Follow Recommended Dosage-Overuse can lead to microbial imbalances, while underuse may not yield expected results [159].

Expanding market value and growth of biofertilizers

With increasing global awareness of sustainable agriculture, the demand for biofertilizers has surged. Consumers, particularly in developing nations, are increasingly prioritizing organic farming, contributing to the expansion of the biofertilizer market. Developed countries such as Spain, Italy, and Germany have also experienced rising demand [160]. The global biofertilizer market was valued at approximately $1.88 billion in 2022 and is projected to reach $3.51 billion by 2027, growing at a Compound Annual Growth Rate (CAGR) of 13.2% [161]. Legume-based nitrogen-fixing inoculants dominate the sector, accounting for around 78% of the market, with phosphate-solubilizing and other bioinoculants comprising 15% and 7%, respectively. India ranks as the fourth-largest consumer of potassium bioinoculants, following the United States, China, and Brazil [162]. North America leads the global market, followed closely by Europe and the Asia-Pacific region. South America is emerging as a key player in the industry. The increasing emphasis on sustainable agriculture and food security continues to drive biofertilizer market expansion worldwide [163].

Future Research Directions for Biofertilizer Innovation

Although biofertilizers are gaining global recognition, further research is needed to enhance their field efficacy. Understanding how beneficial bacteria interact with plant microbiomes is crucial for optimizing their performance under various soil conditions. Researchers should focus on biofertilizers’ ability to modify and enhance the natural microbial ecosystem in plants, leading to improved plant growth and resilience [164]. A significant research gap exists in the study of biofertilizers for forest ecosystems. While coniferous species have been studied to some extent, data on deciduous trees remain scarce. Additionally, many laboratory and greenhouse findings have yet to be successfully translated into field applications. Future studies should explore high-efficiency inoculant strains that can adapt to diverse soil conditions and plant species. Investigating the physiology of rhizobacteria under different soil conditions through in vitro and in vivo studies is essential [165]. Cutting-edge research methods, such as molecular analysis, microbial engineering, biotechnology, and functional genomics, should be leveraged to monitor bacterial colonization and their evolutionary adaptation post-inoculation [166]. Metagenomics, meta transcriptomics, and meta proteomics can provide deeper insights into plant-microbe interactions and their role in plant development. Additionally, genetically engineered strains of plant growth-promoting bacteria have shown promising potential, yet public skepticism regarding their environmental safety remains a barrier to adoption [167]. Researchers and policymakers should work toward educating the public on the safety and advantages of these biofertilizers. Furthermore, biofertilizers should be optimized to sustain microbial life in harsh soil environments while maintaining economic feasibility [168]. Another emerging area is the role of plant prebiotics in biofertilizer efficiency. These compounds act as signaling molecules that attract beneficial bacteria to plant roots. Future research should focus on developing microbial consortia that optimize plantmicrobe interactions for increased agricultural productivity [169]. Establishing a global database of biofertilizer efficacy across various environmental conditions, soil types, and growing seasons would aid in refining application strategies. Moreover, studies have shown that integrating biofertilizers with reduced synthetic nitrogen applications can maintain yield while lowering fertilizer costs [170]. In particular, the JUNCAO nitrogen-fixing biofertilizer has demonstrated improved crop vigor, soil nutrient enhancement, and cost savings. Moving forward, integrating multi-omics approaches with biofertilizer technology can further improve agricultural productivity, ensuring sustainable food production for a growing global population [171].

Conclusion

Biofertilizers offer a sustainable path toward enhancing agricultural productivity while preserving soil health and reducing reliance on synthetic fertilizers. Despite their potential, widespread adoption is limited by challenges such as inconsistent performance, short shelf life, and limited awareness among farmers [172]. Addressing these issues requires advancements in microbial strain selection, formulation techniques, and storage methods to ensure stability and effectiveness. Moreover, a deeper understanding of microbial ecosystems can aid in developing tailored biofertilizers suited to diverse agricultural contexts. Future research should focus on creating efficient delivery systems to support large-scale applications, including reforestation efforts [173]. Embracing biofertilizers is crucial for building a resilient agricultural system that promotes food security, environmental sustainability, and long-term ecosystem health [174-182].

Authors Contributions

All the authors have substantial (equal) contribution in compilation of this review chapter. All authors have read and approved the final manuscript.

Funding

Being a review article, no funding was involved in compilation of the information in this review chapter.

Conflicts of Interest

The authors declare that they have no competing interests.

Ethical Approvals

This study does not involve experiments on animals or human subjects.

Data Availability

This study did not require extensive data collection. For additional information on the subject, the corresponding author can be contacted.

Publisher’s Note

The journal maintains a neutral stance regarding jurisdictional claims associated with the authors’ institutional affiliations.

Acknowledgements

We express our sincere gratitude to my supervisors at Ahmadu Bello University, Zaria, Kaduna State, Nigeria, for their critical review and valuable suggestions, which have significantly enhanced the quality of this manuscript.

References

  1. Hoffmann C, Anette S (2015) Comparison of A1 and A2A receptor dynamics using FRET based receptor sensors. Springer Plus 4(1): 1-32.
  2. Anna MK, Matheus APC, Eiko EK (2016) Acidobacteria strains from subdivision 1 act as plant growth-promoting bacteria. Archives of Microbiology 198(10): 987-993.
  3. Stanislav F, Michal JN, Jennifer A, Robert DP, Jacqueline DF (2007) Analysis of the aerobactin and ferric hydroxamate uptake systems of Yersinia pestis. Microbiology 153(7): 2332-2341.
  4. Liang C, Hao S, Junying H, Dianxuan W, Ke B (2018) Antimicrobial, plant growth-promoting and genomic properties of the peanut endophyte Bacillus velezensis Microbiological Research 218: 41-48.
  5. Kai B, Marnix HM, Daniyal K, Michael AF, Rainer B, et al. (2013) AntiSMASH 2.0-A versatile platform for genome mining of secondary metabolite producers. Nucleic Acids Research 41(W1): W204-W212.
  6. Kai B, Simon S, Kat S, Rasmus V, Nadine Z, et al. (2019) AntiSMASH 5.0: Updates to the secondary metabolite genome mining pipeline. Nucleic Acids Research 47(W1): W81-W87.
  7. Kleinheinz K, Katrine GJ, Larsen MV (2014) Applying the ResFinder and VirulenceFinder web-services for easy identification of acquired antibiotic resistance and coli virulence genes in bacteriophage and prophage nucleotide sequences. Bacteriophage 4(1): e27943.
  8. Turkina MV, Elena V (2019) Bacteria-host crosstalk: Sensing of the quorum in the context of Pseudomonas aeruginosa Journal of Innate Immunity 11(3): 263-279.
  9. Kramer J, Özhan Ö, Kümmerli R (2019) Bacterial siderophores in community and host interactions. Nature Reviews. Microbiology 18(3): 152-163.
  10. Gray EJ, Lee KD, Souleimanov AM, Di FMR, Zhou X (2006) A novel bacteriocin, thuricin 17, produced by plant growth promoting rhizobacteria strain Bacillus thuringiensis NEB17: Isolation and classification. Journal of Applied Microbiology 100(3): 545-554.
  11. Deepak B, Mohammad WA, Ranjan KS, Narendra T (2014) Biofertilizers function as key player in sustainable agriculture by improving soil fertility, plant tolerance and crop productivity. Microbial Cell Factories 13(1): 66-66.
  12. Jolien D, Gia KHH, Katrien DM, Joke P, Ilse F, et al. (2011) Biological control of Rhizoctonia root rot on bean by phenazine and cyclic lipopeptide producing Pseudomonas Phytopathology 101(8): 996-1004.
  13. Fouda AH, Saad ED, Ahmed ME, Emad EDE (2015) Biotechnological applications of fungal endophytes associated with medicinal plant Asclepias sinaica (Bioss.). Annals of Agricultural Sciences 60(1): 95-104.
  14. Kanehisa M, Yoko S, Morishima K (2015) BlastKOALA and GhostKOALA: KEGG tools for functional characterization of genome and metagenome sequences. Journal of Molecular Biology 428(4): 726-731.
  15. Yuan H, Zhang J, Nageswaran D, Li L (2015) Carotenoid metabolism and regulation in horticultural crops. Horticulture Research 2: 15036.
  16. Shin SH, Lim Y, Lee SE, Yang NW, Rhee JH (2001) CAS agar diffusion assay for the measurement of siderophores in biological fluids. J Microbiol Methods 44(1): 89-95.
  17. Kammler M, Schön C, Hantke K (1993) Characterization of the ferrous iron uptake system of Escherichia coli. Journal of Bacteriology 175(19): 6212-6219.
  18. Zaid DS, Shuyun C, Hu C, Ziqi Li, Youguo Li (2022) Comparative genome analysis reveals phylogenetic identity of Bacillus velezensis HNA3 and genomic insights into its plant growth promotion and biocontrol effects. Microbiology Spectrum 10(1): e0216921.
  19. Thiruvengadam R, Gandhi K, Sendhivel V, Harish S, Karthiba L (2022) Complete genome sequence analysis of Bacillus subtilis Bbv57, a promising biocontrol agent against phytopathogens. International Journal of Molecular Sciences 23(17): 9732.
  20. Nelson BA, Preethi R, Alfredo LDL, Ravi K, Austin C, et al. (2014) Complete genome sequence for the Fusarium head blight antagonist Bacillus amyloliquefaciens strain TrigoCor 1448. Genome Announcements 2(2): e00219-e00214.
  21. Dao JG, Rajesh KS, Pratiksha S, Dong PL, Anjney S (2020) Complete genome sequence of Enterobacter roggenkampii ED5, a nitrogen fixing plant growth promoting endophytic bacterium with biocontrol and stress tolerance properties, isolated from sugarcane root. Frontiers in Microbiology 11: 580081.
  22. Subramaniam G, Vivek T, Saxena RK, Srinivas V, Shilp P, et al. (2020) Complete genome sequence of sixteen plant growth promoting Streptomyces strains. Scientific Reports 10(1): 10294.
  23. Adam E, Henry M, Erlacher A, Berg G (2016) Complete genome sequences of the Serratia plymuthica strains 3Rp8 and 3Re4-18, two rhizosphere bacteria with antagonistic activity towards fungal phytopathogens and plant growth promoting abilities. Standards in Genomic Sciences 11(1): 61.
  24. Nasrin S, Hossain JM, Mark RL (2015) Draft genome sequence of Bacillus amyloliquefaciens AP183 with antibacterial activity against methicillin-resistant Staphylococcus aureus. Genome Announcements 3(2): e00162-e00215.
  25. Sakakibara H (2006) Cytokinins: Activity, biosynthesis, and translocation. Annu Rev Plant Biol 57: 431-449.
  26. Sajjad A, Abdul LK, Muhammad AK, Ahmed AH, In JL (2018) Complete genome sequencing and analysis of endophytic Sphingomonas LK11 and its potential in plant growth. 3 Biotech 8(9): 389.
  27. Besaury L, Caroline R (2020) Draft genome sequence of Saccharibacillus sp. strain WB 17, isolated from wheat phyllosphere. Microbiology Resource Announcements 9(7).
  28. Deleu M, Michel P, Nylander T (2008) Effect of Fengycin, a Lipopeptide Produced by Bacillus subtilis, on Model Biomembranes. Biophysical Journal 94(7): 2667-2679.
  29. Vurukonda SSKP, Sandhya V, Shrivastava M, Skz A (2016) Enhancement of drought stress tolerance in crops by plant growth promoting rhizobacteria. Microbiological Research 184: 13-24.
  30. Luck SN, Turner SA, Rajakumar K, Sakellaris H, Adler B (2001) Ferric dicitrate transport system (Fec) of Shigella flexneri 2a YSH6000 is encoded on a novel pathogenicity island carrying multiple antibiotic resistance genes. Infect Immun 69(10): 6012-6021.
  31. Nanjani S, Soni R, Dhiraj P, Hareshkumar K (2022) Genome analysis uncovers the prolific antagonistic and plant growth-promoting potential of endophyte Bacillus velezensis Gene 836: 146671.
  32. Iqbal S, John V, Janjua HA (2021) Genome mining and comparative genome analysis revealed niche-specific genome expansion in antibacterial Bacillus pumilus strain SF-4. Genes 12(7): 1060.
  33. Albarano L, Roberta E, Ruocco N, Costantini M (2020) Genome mining as new challenge in natural products discovery. Marine Drugs 18(4): 199.
  34. Bauman KD, Keelie SB, Moore BS, Chekan JR (2021) Genome mining methods to discover bioactive natural products. Natural Product Reports 38(11): 2100-2129.
  35. Librada AA, Cristopher AB, Christian MH, Luis CM, Pieter CD, et al. (2020) Genome mining, microbial interactions, and molecular networking reveals new dibromoalterochromides from strains of Pseudoalteromonas of coiba national park-panama. Marine Drugs 18(9): 456.
  36. Adeleke BS, Ayansina SA, Babalola OO (2021) Genomic analysis of endophytic Bacillus Cereus T4S and its plant growth-promoting traits. Plants 10(9): 1776.
  37. Chenglong J, Meilin Z, Zirong K, Xue C, Xing W, et al. (2021) Genomic analysis reveals potential mechanisms underlying promotion of tomato plant growth and antagonism of soilborne pathogens by Bacillus amyloliquefaciens Microbiology Spectrum 9(3): e0161521.
  38. Heiko TK, Carlos NLA, Mario W, Mikael LS, Gergely M, et al. (2021) Genomic and Chemical Diversity of Bacillus subtilis Secondary Metabolites against Plant Pathogenic Fungi. mSystems 6(1): e00770-20.
  39. Raturi G, Yogesh S, Rushil M, Surbhi M, Rana N, et al. (2022) Genomic landscape highlights molecular mechanisms involved in silicate solubilization, stress tolerance, and potential growth-promoting activity of bacterium Enterobacter LR6. Cells 11(22): 3622.
  40. Rubén B, Fabricio C, Patricia P (2004) Gibberellin production by bacteria and its involvement in plant growth promotion and yield increase. Applied Microbiology and Biotechnology 65(5): 497-503.
  41. Christopher SH, Matthew D, Aaron AB, Paul MF, Ben L, et al. (2010) High-throughput generation, optimization and analysis of genome-scale metabolic models. Nature Biotechnology 28(9): 977-982.
  42. Yi HS, Yeo RA, Song GC, Ghim YS, Soohyun L, et al. (2016) Impact of a Bacterial Volatile 2,3-Butanediol on Bacillus subtilis Rhizosphere Robustness. Frontiers in Microbiology 7: 993.
  43. Lurthy T, Cantat C, Christian J, Philippe D, Karine G, et al. (2020) Impact of bacterial siderophores on iron status and ionome in pea. Frontiers in Plant Science 11: 730.
  44. Hadj AB, Stéphane C, Livio A, Branislav N, Abdelghani Z (2022) In-depth genome analysis of Bacillus sp. BH32, a salt stress-tolerant endophyte obtained from a halophyte in a semiarid region. Applied Microbiology and Biotechnology 106(8): 3113-3137.
  45. Spaepen S, Jos V, Roseline R (2007) Indole-3-acetic acid in microbial and microorganism-plant signaling. FEMS Microbiol Rev 31(4): 425-448.
  46. Guerrieri MC, Andrea F, Fanfoni E, Tabaglio V, Cocconcelli PS, (2021) Integrated genomic and greenhouse assessment of a novel plant growth-promoting rhizobacterium for tomato plant. Frontiers in Plant Science 12(12): 660620.
  47. Suzanne ED, Tom SM, David EH (2004) Involvement of SirABC in iron-siderophore import in Staphylococcus aureus. Journal of Bacteriology 186(24): 8356-8362.
  48. Maheshwari R, Namita B, Pooja S (2020) Isolation and characterization of ACC deaminase producing endophytic Bacillus mojavensis PRN2 from Pisum sativum. Iran J Biotechnol 18(2): e2308.
  49. Zhao D, Yanqin D, Yanru C, Yanan Z, Liu K, et al. (2022) Isolation and genome sequence of a novel phosphate-solubilizing rhizobacterium Bacillus altitudinis GQYP101 and its effects on rhizosphere microbial community structure and functional traits of corn seedling. Current Microbiology 79(9): 249.
  50. Murata D, Sayaka S, Ohike T, Masahiro, Ano T (2013) Isolation of antifungal bacteria from Japanese fermented soybeans, natto. Journal of Environmental Sciences (China) 25: S127-S131.
  51. Du J, Ma Z, Song J, Xie X, Chen Y, et al. (2014) KEGG-PATH: Kyoto encyclopedia of genes and genomes-based pathway analysis using a path analysis model. Molecular bioSystems 10(9): 2441-2447.
  52. Wang S, Jinbin W, Zhou Y, Huang Y, Tang X (2022) Isolation, classification, and growth-promoting effects of Pantoea YSD J2 from the aboveground leaves of Cyperus esculentus l. var. sativus. Current Microbiology 79(2): 66.
  53. Olanrewaju SO, Bernard RG, Olubukola OB (2017) Mechanisms of action of plant growth promoting bacteria. World J Microbiol Biotechnol 33(11): 197.
  54. Sashidhar B, Podile AR (2010) Mineral phosphate solubilization by rhizosphere bacteria and scope for manipulation of the direct oxidation pathway involving glucose dehydrogenase. Journal of Applied Microbiology 109(1): 1-12.
  55. Scherlach K, Christian H (2021) Mining and unearthing hidden biosynthetic potential. Nature Communications 12(1): 3864.
  56. Baltz RH (2019) Natural product drug discovery in the genomic era: Realities, conjectures, misconceptions, and opportunities. Journal of Industrial Microbiology & Biotechnology 46(3-4): 281-299.
  57. Martín JF, Liras P (2021) Molecular mechanisms of phosphate sensing, transport and signalling in streptomyces and related actinobacteria. Int J Mol Sci 22(3): 1129.
  58. Piccoli P, Rubén B (2013) Terpene production by bacteria and its involvement in plant growth promotion, stress alleviation, and yield increase. Molecular Microbial Ecology of the Rhizosphere pp: 335-343.
  59. Afzal I, Zabta KS, Sikandar S, Shahzad S (2019) Plant beneficial endophytic bacteria: Mechanisms, diversity, host range and genetic determinants. Microbiological Research 221: 36-49.
  60. Kushwaha P, Prem LK, Srivastava AK, Tiwari RK (2019) Plant growth promoting and antifungal activity in endophytic Bacillus strains from pearl millet (Pennisetum glaucum). Brazilian Journal of Microbiology 51(1): 229-241.
  61. Majeed A, Zahir M, Habib A (2018) Plant growth promoting bacteria: Role in soil improvement, abiotic and biotic stress management of crops. Plant Cell Rep 37(12): 1599-1609.
  62. Govind G, Shailendra SP, Narendra KA, Sunil KS, Vinod S (2015) Plant Growth Promoting Rhizobacteria (PGPR): Current and future prospects for development of sustainable agriculture. Journal of Microbial & Biochemical Technology 7(2): 96-102.
  63. Abdel HMS, Amr F, Hesham KAEE, El GAA, Hassan SED (2021) Plant growth-promoting properties of bacterial endophytes isolated from roots of Thymus vulgaris L. and investigate their role as biofertilizers to enhance the essential oil contents. Biomolecular Concepts 12(1): 175-196.
  64. Masunaka A, Mitsuro H, Shigehito T (2011) Plant growth-promoting fungus, trichoderma koningi suppresses isoflavonoid phytoalexin vestitol production for colonization on/in the roots of Lotus japonicus. Microbes Environ 26(2): 128-134.
  65. Santoyo G, Gabriel MH, Carmen MDOM, Bernard RG (2015) Plant growth-promoting bacterial endophytes. Microbiological Research 183: 92-99.
  66. Himanshu D, Neha V, Yogita L, Priyam M, Dev KS (2021) Polyphasic characterization of and genomic insights into a haloalkali-tolerant Saccharibacillus alkalitolerans Nov., that produces three cellulase isozymes and several antimicrobial compounds. Antonie van Leeuwenhoek 114(7): 1043-1057.
  67. Shih FF, Pei FS, Hsueh YL, Jyuan YW, Hong SX, et al. (2016) Plant growth-promoting traits of yeasts isolated from the phyllosphere and rhizosphere of Drosera spatulata Fungal Biology 120(3): 433-448.
  68. Huang AC, Anne O (2019) Plant terpenes that mediate below-ground interactions: Prospects for bioengineering terpenoids for plant protection. Pest Management Science 75(9): 2368-2377.
  69. Pablo RH, Leo SO, Jan DE (2008) Properties of bacterial endophytes and their proposed role in plant growth. Trends in Microbiology 16(10): 463-471.
  70. Lingmin J, Jae CJ, Jung SL, Jeong MP, Jung WY, et al. (2019) Potential of Pantoea dispersa as an effective biocontrol agent for black rot in sweet potato. Scientific Reports 9(1): 16354.
  71. Riseh RS, Marzieh EZ, Mozghan GV, Yury AS (2021) Reducing drought stress in plants by encapsulating plant growth-promoting bacteria with polysaccharides. Int J Mol Sci 22(23): 12979.
  72. Asghar H, Zahir Z, Arshad M, Khaliq A (2002) Relationship between in vitro production of auxins by rhizobacteria and their growth-promoting activities in Brassica juncea L. Biology and Fertility of Soils 35(4): 231-237.
  73. Benjamin PB, Jasmin P, Sonia G, Eiji N (2021) Role of basal ABA in plant growth and development. Genes 12(12): 1936.
  74. Vejan P, Abdullah R, Khadiran T, Ismail S, Amru NB (2016) Role of plant growth promoting rhizobacteria in agricultural sustainability-a review. Molecules 21(5): 573.
  75. Sun JQ, Wang XY, Wang LJ, Lian X, Min Liu, et al. (2015) Saccharibacillus deserti Nov., isolated from desert soil. International Journal of Systematic and Evolutionary Microbiology 66(2): 623-627.
  76. Kämpfer PB, Hans J, Kleinhagauer T, McInroy JA, Glaeser SP (2016) Saccharibacillus endophyticus Nov., an endophyte of cotton. International Journal of Systematic and Evolutionary Microbiology 66(12): 5134-5139.
  77. Yang SY, Huan L, Rui Liu Zhang KY, Lai R (2009) Saccharibacillus kuerlensis nov., isolated from a desert soil. Int J Syst Evol Microbiol 59(5): 953-957.
  78. Hui H, Shan G, Qi W, Lin YH, Xia FS (2016) Saccharibacillus qingshengii Nov., isolated from a lead-cadmium tailing. International Journal of Systematic and Evolutionary Microbiology 66(11): 4645-4649.
  79. Rivas R, Paula GF, Jose Luis ZP, Pedro FM, Eustoquio MM, et al. (2008) Saccharibacillus sacchari nov., sp. nov., isolated from sugar cane. International Journal of Systematic and Evolutionary Microbiology 58(8): 1850-1854.
  80. Ellermann M, Janelle CA (2016) Siderophore-mediated iron acquisition and modulation of host-bacterial interactions. Free Radical Biology & Medicine 105: 68-78.
  81. Sulochana MB, Jayachandra SY, Anil KS, Parameshwar AB, Mohan RK, et al. (2014) Siderophore as a potential plant growth-promoting agent produced by Pseudomonas aeruginosa JAS-25. Applied Biochemistry and Biotechnology 174(1): 297-308.
  82. Lee KD, Elizabeth JG, Fazli M, Jung WJ, Charles T, et al. (2008) The class IId bacteriocin thuricin-17 increases plant growth. Planta 229(4): 747-755.
  83. Opeyemi KA, Noelle HOD, Alberto DS, Andrew JL (2021) The complete genome sequence of Hafnia alvei A23BA; a potential antibiotic-producing rhizobacterium. BMC Research Notes 14(1): 1-4.
  84. Fiodor A, Surender S, Pranaw K (2021) The contrivance of plant growth promoting microbes to mitigate climate change impact in agriculture. Microorganisms 9(9): 1841.
  85. Susanne G, Sieu LT, Gregory MC (2006) The Phn system of Mycobacterium smegmatis: A second high-affinity ABC-transporter for phosphate. Microbiology 152(11): 3453-3465.
  86. Swapnil P, Mukesh M, Sandeep KS, Dhuldhaj U, Harish, et al. (2021) Vital roles of carotenoids in plants and humans to deteriorate stress with its structure, biosynthesis, metabolic engineering and functional aspects. Current Plant Biology 26(1): 100203.
  87. Liu W, Wang Q, Jinyu H, Chen T, Luo Y, et al. (2016) Whole genome analysis of halotolerant and alkalotolerant plant growth-promoting rhizobacterium Klebsiella D5A. Scientific Reports 6: 26710.
  88. Singh P, Rajesh KS, Guo DJ, Sharma A, Ram NS, et al. (2021) Whole genome analysis of sugarcane root-associated endophyte Pseudomonas aeruginosa B18-A plant growth-promoting bacterium with antagonistic potential against Sporisorium scitamineum. Frontiers in Microbiology 12: 628376.
  89. Amaresh C, Priyanka C, Pramila T (2021) Whole genome sequence insight of two plant growth-promoting bacteria ( subtilis BS87 and B. megaterium BM89) isolated and characterized from sugarcane rhizosphere depicting better crop yield potentiality. Microbiological Research 247: 126733.
  90. Saha J, Sourav D, Pal Ayon (2022) Whole genome sequencing and comparative genomic analyses of Pseudomonas aeruginosa strain isolated from arable soil reveal novel insights into heavy metal resistance and codon biology. Curr Genet 68(3-4): 481-503.
  91. Olubukola OB, Bartholomew SA, Ayansina SA (2021) Whole genome sequencing of sunflower root-associated Bacillus cereus. Evolutionary Bioinformatics p. 17.
  92. Rikame T, Mahesh B (2022) Whole genome, functional annotation and comparative genomics of plant growth-promoting bacteria Pseudomonas aeruginosa (NG61) with potential application in agro-industry. Current Microbiology 79(6): 169.
  93. Lingmin J, Jae CJ, Jung SL, Jeong MP, Jung WY, et al. (2019) Potential of Pantoea dispersa as an effective biocontrol agent for black rot in sweet potato. Scientific Reports 9(1): 16354.
  94. Lingmin J, Chan JL, Jae CJ, Cha YK, Dae HK, et al. (2019) Whole-genome sequence data and analysis of Saccharibacillus ATSA2 isolated from Kimchi cabbage seeds. Data in Brief 26: 104465.
  95. Lingmin J, Chan JL, Song GK, Jae CJ, Cha YK, et al. (2019) Saccharibacillus brassicae Nov., an endophytic bacterium isolated from kimchi cabbage (Brassica rapa subsp. Pekinensis) seeds. Journal of Microbiology (Seoul, Korea) 58(1): 24-29.
  96. Shengye G, Xingyu L, Pengfei H, Honhing H, Yixin W, et al. (2015) Whole-genome sequencing of Bacillus subtilis XF-1 reveals mechanisms for biological control and multiple beneficial properties in plants. Journal of Industrial Microbiology & Biotechnology 42(6): 925-937.
  97. Farhad H, Ali S, Hemmatollah P, Seyyed AM, Modarres S (2012) A comparison between foliar application and seed inoculation of biofertilizers on canola (Brassica napus L.) grown under waterlogged conditions. Australian Journal of Crop Science 6(10): 1435-1440.
  98. Mohammad WA, Dipesh KT, Ranjan KS, Sarvajeet SG, Narendra T (2013) A critical review on fungi mediated plant responses with special emphasis to Piriformospora indica on improved production and protection of crops. Plant Physiology and Biochemistry 70: 403-410.
  99. Martinez AI, Richard L, Dixon R (2004) A crucial arginine residue is required for a conformational switch in NifL to regulate nitrogen fixation in Azotobacter vinelandii. Proc Natl Acad Sci USA 101(46): 16316-16321.
  100. Simpson FB, Burris RH (1984) A nitrogen pressure of 50 atmospheres does not prevent evolution of hydrogen by nitrogenase. Science 224(4653): 1095-1097.
  101. Thorneley RN, Ashby G, Millar NC, Gutfreund H (1989) A transient-kinetic study of the nitrogenase of Klebsiella pneumoniae by stopped-flow calorimetry. Comparison with the myosin ATPase. The Biochemical Journal 264(3): 657-661.
  102. Utsumi Y, Chikako U, Tanaka M, Van HC, Takahashi S, et al. (2019) Acetic acid treatment enhances drought avoidance in cassava (Manihot esculenta Crantz). Frontiers in Plant Science 10: 521-521.
  103. Winanda H, Arinthip T, Wasu P, Kannika D (2016) Actinomycetes from Eucalyptus and their biological activities for controlling Eucalyptus leaf and shoot blight. Microbiological Research 188: 42-52.
  104. Ludden PW, Burris RH (1976) Activating factor for the iron protein of nitrogenase from Rhodospirillum rubrum. Science 194(4263): 424-426.
  105. Fasusi OA, Cristina C, Babalola OO (2021) Agricultural sustainability: Microbial biofertilizers in rhizosphere management. Agriculture 11(2):163.
  106. Umesh KB, Madhulika S, Peddisetty PS, Sangeeta P, Sellamuthu G, et al. (2017) An environmentally friendly engineered Azotobacter Strain that replaces a substantial amount of urea fertilizer while sustaining the same wheat yield. Applied and Environmental Microbiology 83(15): e00590-17.
  107. Phour M, Satyavir SS (2020) Amelioration of salinity stress and growth stimulation of mustard (Brassica juncea) by salt-tolerant Pseudomonas species. Applied Soil Ecology 149: 103518.
  108. Yu X, Li Y, Cui Y, Liu R, Chen Q, et al. (2017) An indoleacetic acid-producing Ochrobactrum MGJ11 counteracts cadmium effect on soybean by promoting plant growth. Journal of Applied Microbiology 122(4): 987-996.
  109. Kranz RG, Haselkorn R (1986) Anaerobic regulation of nitrogen-fixation genes in Rhodopseudomonas capsulata. PNAS 83(18): 6805-6809.
  110. Zehnder GW, John FM, Sikora EJ, Kloepper JW (2001) Application of rhizobacteria for induced resistance. European Journal of Plant Pathology 107: 39-50.
  111. Saxena B, Kamlesh S, Giri B (2017) Arbuscular mycorrhizal fungi and tolerance of salt stress in plants. In Arbuscular Mycorrhizas and Stress Tolerance of Plants, pp: 67-97.
  112. Paul S, Vaishali S, Prabhat KC, Abhishek KS, Sudheer KU (2020) Assessment of carrot growth performance with inoculation of AsT-PGPR under arsenic infested zone. G-Journal of Environmental Science and Technology 7(6): 78-84.
  113. Ortiz MJCF, Mauro DN, Maria DLAD, Leonardo C (2012) Association with an ammonium-excreting bacterium allows diazotrophic culture of oil-rich eukaryotic microalgae. Applied and Environmental Microbiology 78(7): 2345-2352.
  114. Robson RL, Robert J, Moyra RR, Ariel S, Toby HR (2015) Azotobacter genomes: The genome of Azotobacter chroococcum NCIMB 8003 (ATCC 4412). PLoS One 10(6): e0127997.
  115. Hill S, Austin S, Eydmann T, Jones T, Dixon R (1996) Azotobacter vinelandii NIFL is a flavoprotein that modulates transcriptional activation of nitrogen-fixation genes via a redox-sensitive switch. Proceedings of the National Academy of Sciences of the United States of America 93(5): 2143-2148.
  116. Konopka JB (2012) N-Acetylglucosamine functions in cell signaling. Scientifica p.489208.
  117. Das HK (2019) Azotobacters as biofertilizer. Advances in Applied Microbiology 108: 1-43.
  118. Kwon JH, Sang JW, Moon JH, Lee U, Park YS, et al. (2021) Bacillus licheniformis PR2 controls fungal diseases and increases production of jujube fruit under field conditions. Horticulturae 7(3): 49.
  119. Zhou C, Jingjing Z, Qian N, Jiansheng G, Congsheng Y (2021) Bacillus subtilis SL18r induces tomato resistance against botrytis cinerea, involving activation of long non-coding RNA, MSTRG18363 to decoy miR1918. Frontiers in Plant Science 11: 634819.
  120. Grobelak A, Joanna H (2017) Bacterial siderophores promote plant growth: Screening of catechol and hydroxamate siderophores. International Journal of Phytoremediation 19(9): 825-833.
  121. Haddock BA, Jones CW (1977) Bacterial Respiration. Bacteriological Reviews 41(1): 47-99.
  122. Igiehon NO, Olubukola OB (2018) Below-ground-above-ground plant-microbial interactions: Focusing on soybean, rhizobacteria and mycorrhizal fungi. The Open Microbiology Journal 12(1): 261-279.
  123. Nihorimbere V, Marc O, Smargiassi Maïté, Thonart Philippe (2011) Beneficial effect of the rhizosphere microbial community for plant growth and health. Biotechnologie, Agronomie, Société et Environnement 15(2): 327-337.
  124. Verma S, Abhishek S, Swati SP, Singh RK, Singh JP (2017) Bio-efficacy of organic formulations on crop production-A review. International Journal of Current Microbiology and Applied Sciences 6(5): 648-665.
  125. Ye L, Xia Z, Encai B, Li J, Zou Z, et al. (2020) Bio-organic fertilizer with reduced rates of chemical fertilization improves soil fertility and enhances tomato yield and quality. Scientific Reports 10: 177.
  126. Marty RJ, Valerie LC, Mary CW, Nancy FL, William EN, et al. (1989) Biochemical and genetic analysis of the nifUSVWZM cluster from Azotobacter vinelandii. Molecular & General Genetics 219(1): 49-57.
  127. Naher UA, Qurban AP, Othman R, Ismail MR, Berahim Z (2016) Biofertilizer as a supplement of chemical fertilizer for yield maximization of rice. Journal of Agriculture Food and Development 2(1): 16-22.
  128. Maria A, Hafiza IA, Rashid S, Asna A, Muniba T, et al. (2018) Biofertilizer as an alternative for chemical fertilizers. Research & Reviews: Journal of Agriculture and Allied Sciences 7(1): 1-7.
  129. Sneha S, Anitha B, Sahair RA, Raghu T, Gopenath TS, et al. (2018) Biofertilizer for crop production and soil fertility. Academia Journal of Agricultural Research 6(8): 299-306.
  130. Yadav KK, Smritikana S (2019) Biofertilizers impact on soil fertility and crop productivity under sustainable agriculture. Environment and Ecology 37(1): 89-93.
  131. Brill WJ (1977) Biological nitrogen fixation. Scientific American 236(3): 68-81.
  132. Burris RH (1966) Biological nitrogen fixation. Annual Review of Plant Physiology 17(1): 155-184.
  133. Rubio LM, Paul WL (2008) Biosynthesis of the iron-molybdenum cofactor of nitrogenase. Annual Review of Microbiology 62: 93-111.
  134. Nag P, Subrata P (2012) Fe protein over-expression can enhance the nitrogenase activity of Azotobacter vinelandii. Journal of Basic Microbiology 53(2): 156-162.
  135. Elmerich C (2015) One hundred years discovery of nitrogen‐fixing rhizobacteria. Biological Nitrogen Fixation pp. 897-912.
  136. Newton WE (2015) Recent advances in understanding nitrogenases and how they work. Biological Nitrogen Fixation pp. 5-20.
  137. Poza CC, Carlos EE, Luis MR (2015) Regulation of nif gene expression in Azotobacter vinelandii. Biological Nitrogen Fixation pp: 99-108.
  138. Nieto KF, William TF (1989) Biosynthesis of cytokinins by Azotobacter chroococcum. Soil Biology and Biochemistry 21(7): 967-972.
  139. Ramprasad NK, Ramesh C, Navneet P, Kiran PR (2019) Carrier-based and liquid bioinoculants of Azotobacter and PSB saved chemical fertilizers in wheat (Triticum aestivum L.) and enhanced soil biological properties in Mollisols. Journal of Plant Nutrition 43(1): 36-50.
  140. Latković D, Jelena M, Zoran D, Pivic R, Aleksandsar S, et al. (2020) Case study upon foliar application of biofertilizers affecting microbial biomass and enzyme activity in soil and yield related properties of maize and wheat grains. Biology 9(12): 452.
  141. Smith BE, Raymond RL, Newton WE (2004) Catalysts for Nitrogen Fixation p. 340.
  142. Anahita BD, Mohammad MS, Maryam Z, Naeimeh E (2020) Changes in soil microbial activity, essential oil quantity, and quality of Thai basil as response to biofertilizers and humic acid. Journal of Cleaner Production 256: 120439.
  143. Ravi KG, Gaurav B, Jaspal S, Sudhir KU, Singh AP (2013) Combined effects of plant growth promoting rhizobacteria and fungi on mung bean (Vigna radiata L.). International Journal of Pharmaceutical Sciences and Research 4(11): 4422-4426.
  144. Mahato S, Asmita K (2018) Comparative study of Azotobacter with or without other fertilizers on growth and yield of wheat in Western hills of Nepal. Annals of Agrarian Science 16(3): 250-256.
  145. Lasbleiz M, Karine L, Leanne KA, Urania C, Georges C, et al. (2016) Composition of diatom communities and their contribution to plankton biomass in the naturally iron-fertilized region of kerguelen in the southern ocean. FEMS Microbiol Ecol 92(11): fiw171.
  146. Jason B, Pampa R, André S, Richard L, Ray D (2001) Concerted inhibition of the transcriptional activation functions of the enhancer‐binding protein NIFA by the anti‐activator NIFL. Molecular Microbiology 39(2): 480-494.
  147. Amara C, Adnan A, Xiaofen W, Fanta Y, Yuegao H (2019) Contrasting impacts of long-term application of biofertilizers and organic manure on grain yield of winter wheat in north China plain. Agronomy 9(6): 312.
  148. Walters DR, Jaan R, Neil DH (2013) Controlling crop diseases using induced resistance: Challenges for the future. J Exp Bot 64(5): 1263-1280.
  149. Mendes R, Marco K, Irene DB, Ester D, Menno VDV, et al. (2011) Deciphering the rhizosphere microbiome for disease-suppressive bacteria. Science 332(6033): 1097-1100.
  150. Spadaro D, Samir D (2016) Development of biocontrol products for postharvest diseases of fruit: The importance of elucidating the mechanisms of action of yeast antagonists. Trends in Food Science & Technology 47: 39-49.
  151. Sawah AM, Hauka FIA, Aida HA (2018) Dual inoculation with Azotobacter chroococcum MF135558 and Klebsiella oxytoca MF135559 enhance the growth and yield of wheat plant and reduce N-fertilizers usage. Journal of Food and Dairy Sciences 3(3): 67-76.
  152. Sae KS, Ahmed AS, Ismael AH, Hamed AP (2015) Effect of bio-fertilizer and chemical fertilizer on growth and yield in cucumber (Cucumis sativus) in green house condition. Pakistan Journal of Biological Sciences 18(3): 129-134.
  153. Obid SA, Idris AE, Badr EAMA (2016) Effect of bio-fertilizer on growth and yield of two maize (Zea mays ) cultivars at shambat, Sudan. Scholars Journal of Agriculture and Veterinary Sciences 3(4): 313-317.
  154. Padhiary GG, Dubey AK (2020) Effect of bio-fertilizers on growth, yield and yield attributing characters of brinjal. International Journal of Current Microbiology and Applied Sciences 9(3): 1643-1647.
  155. Djajadi NSR, Hidayati SN (2020) Effect of NPK fertilizer, biofertilizer containing N fixer and P solubilizer, and green manure of juncea on nutrients uptake and growth of sugarcane. IOP Conference Series: Earth and Environmental Science 418(1): 012068.
  156. Kumar V, Behl RK, Narula N (2001) Effect of phosphate-solubilizing strains of Azotobacter chroococcum on yield traits and their survival in the rhizosphere of wheat genotypes under field conditions. Acta Agronomica Hungarica 49(2): 141-149.
  157. Yang ZH, Stoven K, Haneklaus S, Singh BR, Schnug E (2010) Elemental sulfur oxidation by Thiobacillus and aerobic heterotrophic sulfur-oxidizing bacteria. Pedosphere 20(1): 71-19.
  158. Eder JO, Carolina VM, Saulo TA, Agnaldo RMC, Rafaela PA, et al. (2017) Evaluation of cassava germplasm for drought tolerance under field conditions. Euphytica 213(8): 188.
  159. Dutta J, Debajit T (2017) Evaluation of multifarious plant growth promoting traits, antagonistic potential and phylogenetic affiliation of rhizobacteria associated with commercial tea plants grown in Darjeeling, India. PloS One 12(8): e0182302.
  160. Upadhyay SK, Singh JS, Devendra PS (2011) Exopolysaccharide-producing plant growth-promoting rhizobacteria under salinity condition. Pedosphere 21(2): 214-222.
  161. Ajinath SD, Sangeeta P, Eyarkai NV, Ram KG, Rajbir S, et al. (2018) Exploitation of microbial antagonists for the control of postharvest diseases of fruits: A review. Critical Reviews in Food Science and Nutrition 59(9): 1498-1513.
  162. Islam AAED, Sarosh B, Johan M (2014) Improved heat stress tolerance of wheat seedlings by bacterial seed treatment. Plant and Soil 379(1): 337-350.
  163. Schütz L, Andreas G, Meier M, Müller A, Boller T, et al. (2018) Improving crop yield and nutrient use efficiency via biofertilization-A global meta-analysis. Front Plant Sci 8: 2204.
  164. Pourya M, Jahanshir S, Mozhgan MT, Amin S, Jose ES (2020) Induced resistance in wheat Triticum aestivum by chemical- and bio-fertilizers against english aphid Sitobion avenae (Fabricius) (Hemiptera: Aphididae) in greenhouse. International Journal of Tropical Insect Science 40(4): 1043-1052.
  165. Elsharkawy MM, Shimizu M, Takahashi H, Hyakumachi M (2012) Induction of systemic resistance against Cucumber mosaic virus by Penicillium simplicissimum GP17‐2 in Arabidopsis and tobacco. Plant Pathology 61(5): 964-976.
  166. Howell CR, Hanson LE, Stipanovic RD, Puckhaber LS (2000) Induction of terpenoid synthesis in cotton roots and control of Rhizoctonia solani by seed treatment with Trichoderma virens. Phytopathology 90(3): 248-252.
  167. Ramesh A, Sushil KS, Mahaveer PS, Namrata Y, Joshil OP (2014) Inoculation of zinc solubilizing Bacillus aryabhattai strains for improved growth, mobilization and biofortification of zinc in soybean and wheat cultivated in vertisols of central India. Applied Soil Ecology 73: 87-96.
  168. Sah S, Nahar S, Rajni S (2017) Iron acquisition in maize (Zea mays ) using Pseudomonas siderophore. 3 Biotech 7(2): 121.
  169. Mukhtar T, Shafiq UR, Smith D, Sultan T, Mahmoud FS, et al. (2020) Mitigation of heat stress in Solanum lycopersicum l. by acc-deaminase and exopolysaccharide producing Bacillus cereus: Effects on biochemical profiling. Sustainability 12(6): 2159.
  170. Christopher B, Mathilde NC, Ákos TK (2020) Molecular aspects of plant growth promotion and protection by Bacillus subtilis. Molecular Plant-Microbe Interactions 34(1): 15-25.
  171. Rodrigues AA, Marcus VF, Renan DSS, Serigo TS, Jose DGV (2016) Isolation and selection of plant growth-promoting bacteria associated with sugarcane. Res Agro Trop 46(2): 149-158.
  172. Medhora M, Phadnis SH, Das HK (1983) Construction of a gene library from the nitrogen-fixing aerobe Azotobacter vinelandii. Gene 25(2-3): 355-360.
  173. Madden MS, Kindon ND, Ludden PW, Shah VK (1990) Diastereomer-dependent substrate reduction properties of a dinitrogenase containing 1-fluorohomocitrate in the iron-molybdenum cofactor. Proc Natl Acad Sci 87(17): 6517-6521.
  174. Kim J, Douglas CR (1992) Crystallographic structure and functional implications of the nitrogenase molybdenum-iron protein from Azotobacter vinelandii. Nature 360(6404): 553-560.
  175. Kelly MJ, Robert KP, Yates MG, Kennedy C (1990) Cloning and mutagenesis of genes encoding the cytochrome bd terminal oxidase complex in Azotobacter vinelandii: Mutants deficient in the cytochrome d complex are unable to fix nitrogen in air. Journal of Bacteriology 172(10): 6010-6019.
  176. Baker R (1991) Diversity in biological control. Crop Protection 10(2): 85-94.
  177. Blatny JM, Brautaset T, Winther LHC, K Haugan, Valla S (1997) Construction and use of a versatile set of broad-host-range cloning and expression vectors based on the RK2 replicon. Applied and Environmental Microbiology 63(2): 370-379.
  178. Detroy RW, Witz DF, Parejko RA, Wilson PW (1967) Complementary functioning of two components required for the reduction of n2 from four nitrogen-fixing bacteria. Science 158(3800): 526-527.
  179. Emerich DW, Burris RH (1978) Complementary functioning of the component proteins of nitrogenase from several bacteria. Journal of Bacteriology 134(3): 936-943.
  180. Golden JW, Carrasco CD, Mulligan ME, Schneider GJ, Haselkorn R (1988) Deletion of a 55-kilobase-pair DNA element from the chromosome during heterocyst differentiation of Anabaena sp. Strain PCC 7120. Journal of Bacteriology 170(11): 5034-5041.
  181. Hau HH, Pei RC, Fan CH, Shih HH, Chih HK (2021) A Plant endophytic bacterium, Burkholderia seminalis strain 869t2, promotes plant growth in arabidopsis, pak choi, chinese amaranth, lettuces, and other vegetables. Microorganisms 9(8): 1703.
  182. Vela GR, Rosenthal RS (1972) Effect of peptone on Azotobacter Journal of Bacteriology 111(1): 260-266.

© 2025 Ehime Itamah. This is an open access article distributed under the terms of the Creative Commons Attribution License , which permits unrestricted use, distribution, and build upon your work non-commercially.

About Crimson

We at Crimson Publishing are a group of people with a combined passion for science and research, who wants to bring to the world a unified platform where all scientific know-how is available read more...

Leave a comment

Contact Info

  • Crimson Publishers, LLC
  • 260 Madison Ave, 8th Floor
  •     New York, NY 10016, USA
  • +1 (929) 600-8049
  • +1 (929) 447-1137
  • info@crimsonpublishers.com
  • www.crimsonpublishers.com