Abstract
Plant health is essential for food security, and constitutes a major predictor to safe and sustainable food systems. Over 40% of the global crops' productions are lost to pests, insects, diseases, and weeds, while the routinely used chemical-based pesticides to manage the menace also have detrimental effects on the microbial communities and ecosystem functioning. The rhizosphere serves as the microbial seed bank where microorganisms transform organic and inorganic substances in the rhizosphere into accessible plant nutrients as plants harbor diverse microorganisms such as fungi, bacteria, nematodes, viruses, and protists among others. Although, the pathogenic microbes initiate diseases by infiltrating the protective microbial barrier and plants' natural defense systems in the rhizosphere. Whereas, the process is often circumvented by the beneficial microorganisms which antagonize the pathogens to instill disease resistance. The management of plant health through approaches focused on disease prevention is instrumental to attaining sustainable food security, and safety. Therefore, an in-depth understanding of the evolving and succession of root microbiomes in response to crop development as discussed in this review opens up new-fangled possibilities for reaping the profit of beneficial root–microbiomes' interactions toward attaining sustainable plant health.
Introduction
Agricultural management practices, such as crop rotation, fertilizer application, and land tilling modify soil physical and chemical properties, amidst diverse interacting forces which shape soil microbial populations (Schmidt et al., 2019). The important plant microbiomes can be categorized into aboveground and belowground. The phyllosphere/phyllobiome characterized by the aboveground is made up of leaves, stems, and reproductive organs, while the rhizosphere/rhizobiome which consists of the belowground is the roots' part and the associated soil (Lucaciu et al., 2019). The interactions between plant roots and microorganisms have a direct impact on the soil, and the rhizosphere region is the home to diverse microorganisms (Adedeji and Babalola, 2020), and a “hot spot” of intensive microbial activity (Dai et al., 2019). The plant microbiome consists of a variety of microbes such as bacteria, fungi, protists, archaea, and viruses that reside on or inside their host plants (Zhang et al., 2021). Rhizosphere-associated microbes have an extensive variety of metabolic abilities and play an important role in the rhizosphere environment, such as organic matter breakdown and nutrient cycling, both of which benefit plant growth and health. More importantly, the microbial population aids plant development and responds to a range of environmental conditions (Dai et al., 2019).
Plants are key sources of energy input in a plant-soil subsystem, providing nutrients and carbon for heterotrophic microbial communities in the form of root exudates and litter deposits (Shanmugam and Kingery, 2018). Through rhizodeposition which is a major phenomenon that occurs in the rhizosphere, high- and low-molecular-weight compounds including secondary metabolites, organic acids, amino acids, sugars, vitamins, and polysaccharides are released into the surrounding soil in the form of exudates. This increases the richness of microbiological and functional diversity, leading to the formation of extremely lively and unique microbial communities linked with plant roots (Chukwuneme et al., 2021). Although the microbiome is made up of a variety of organisms, most research on microbial function in disease prevention and plant health has concentrated on fungi and bacteria (Xiong et al., 2020).
As reported in a recent study, soil and climatic characteristics are significant determinants of microbial community composition, variety, and metabolic potential in a range of the surroundings (Lladó et al., 2018). This is a result of the swift response of the microbes to abiotic and biotic changes. Hence, the structure and function of soil microbial communities are frequently utilized as pointers for determining soil fertility and quality (Enagbonma et al., 2020). Further insights into the essential functions of rhizosphere microbiomes and plant genetic characteristics under various situations have been accessed through the advent of OMICS technology which is based on Next-Generation Sequencing (NGS) (Pramanik et al., 2020), and provides the gateway to attaining sustainable plant health.
The plant rhizospheric zone is a niche of microbial activity based on the resistance of the root system against phytopathogens. The region provides a variety of benefits to plant health both directly and indirectly (Gupta et al., 2019). It is generally recognized that soil microbes serve as a primary nutrient reservoir for plants through their active participation in nutrient cycle processes such as nitrogen cycling, organic matter decomposition and mineral weathering, all of which influence plant growth (Jilling et al., 2018). Thus, plant roots and microbe interactions are critical for plant participation in the ecosystem's functioning. Understanding ecosystem responses to the changing environments require knowledge of microbial diversity distribution and functions. More so, root exudates contain an extensive variety of chemicals, including amino acids, carbohydrates, siderophores, and enzymes, that can reinforce the activities of the microbial community and significantly change the structure of the rhizospheric microbial community, contingent on the plant species and genotype (Wei et al., 2017). Plant-associated microbial communities promote plant development and resilience to diverse abiotic and biotic stressors. Soil microbial species through their roles in carbon sequestration and biogeochemical cycling play important roles in the mitigation of climate change that presently constitutes a global concern (Dubey et al., 2019). Improved ability to predict functionality from dynamic aberrations in root microbial composition is critical for building “designer” microbiome interventions and enhancing agricultural production and sustainability. This will necessitate a more comprehensive genomic and functional classification of plant-linked microbes, their genetic factor, and plant-microbe interactions for their exact useful roles (Richardson et al., 2021).
Beneficial, commensal, or pathogenic relationships exist between specific microorganisms and their plant hosts. Plant microbiomes, in many instances, show a beneficial role at the community level, protecting plants from pathogens, while also boosting growth, health, and providing plants with an adaptive edge (Zhang et al., 2021). Therefore, the interactions between plants and their microbiota are intricate and constantly changing (Fausto et al., 2018). This interaction and interdependence on the abiotic and biotic components of the soil environment can be explained by the plant-soil feedback mechanism, as shown by Shanmugam and Kingery (2018).
Plant defense system: Abating the invasion of pathogens by the rhizospheric microbiome
Plant diseases have caused serious economic and nutritional crises in the past and are still responsible for significant losses in global crop production today (Chun and Chandrasekaran, 2019). Among the factors that contribute to production loss, pests and diseases constitute major global damages (Ab-Rahman et al., 2018). As a result of the unrestrained and widespread use of artificial agrochemicals for plant protection and growth, environmental pollution has become a serious problem. Agrochemical use indefinitely has various negative consequences, including increasing resistance in plant pathogenic microorganisms, detrimental impacts on non-target organisms, and deterioration of soil health (Choudhary et al., 2017). When it comes to plant disease, there is a complex interplay between the host plant and the pathogen, and the resistance/susceptibility response might include a variety of factors (Kumar and Dubey, 2020). Disease suppressive soils are the most visible example of microbe-mediated plant defense against pathogen infection in agricultural soils Meanwhile, structures such as the physical and chemical barriers, quick active defenses, passive and delayed active defenses including the non-host resistance, all cumulate to plant defense systems. However, the rapid active defenses entail changes in cell wall reinforcement, membrane function, the hypersensitive reaction, and the initial oxidative burst which results in phytoalexins, and programmed cell death.
Systemic acquired resistance, pathogenesis-related gene expression, pathogen containment, and wound repair are all examples of delayed active defenses (SAR). Salicylic acid, which is required for defense against SAR and biotrophic pathogens, along with ethylene and jasmonic acid are both involved in defense against necrotrophic pathogens in addition to beneficial plant-microbe interactions, such as induced systemic resistance (ISR) and priming as examples of plant defense signaling molecules (Ab-Rahman et al., 2018). Our ability to control and modify the rhizosphere microbiota is currently restricted. Inoculation is the most direct technique to change the microbiome (Kumar and Dubey, 2020). For decades, commercially accessible products comprising of one or more kinds of fungi or bacteria have been available. The majority of these species, however, were obtained using typical culturing methods that do not mimic the chemical milieu of soil. Other options include adding organic materials to soils that contain diverse but undefined microbial mixes in the hopes of improving function and pathogen resistance. In this case, the capacity of beneficial inoculants could be limited to spread (Alori et al., 2017). Plant breeding or engineering features are other techniques to engineer the rhizosphere. We will be able to engineer root architecture, specific root exudates, or other plant qualities that support beneficial microbiomes into crops using CRISPR and other gene-editing technologies as we identify root architecture, specific root exudates, or other plant traits that support beneficial microbiomes. This technology has been effectively explored in safeguarding plants against both biotic and abiotic stress. An instance is the production of rice lines which has broad-spectrum resistance to Xanthomonas oryzae pv. oryzae that resulted in the modification of the promoter region of O. sativa SWEET11, O. sativa SWEET13, and O. sativa SWEET14 (Oliva et al., 2019), while other studies have also investigated the plant—microbe interactions with the use of CRISPR-Cas (Shelake et al., 2019). This method appears promising because it mimics the interactions that sustain beneficial microorganisms in natural systems and that have been designated through holobiont development (Wallenstein, 2017; Thomashow et al., 2019). Chemical pesticides are now widely employed to ensure long-term productivity and harvest, stressing the widespread usage of phytochemical pesticides. Nonetheless, these chemical pesticide tactics have negative consequences for crops, the environment, and the health of both farming communities and consumer populations. As a result, alternative and long-term disease methods are required. An alternative pest control strategy using bio-pesticides instead of synthetic or chemical pesticides poses a positive phenomenon in reducing pest threat with prevention of chemical residue deposition, reduced toxicity, combinatorial optimal attributes on efficacy, and reduced environmental impacts in the realm of humans and the environment affecting only the pests will positively have an impact (Chun and Chandrasekaran, 2019). In some recent studies, the success of biopesticde formulations from varying Trichoderma species were reported effective in the management of tomoto root rot diseases (Olowe et al., 2022), while Mishra et al. (2022) found that the use of 2,4- DAPG-producing P. fluorescens JM-1 suppressd F. monoliforme-causing ear rot diseases in maize and the PGP features of P. fluorescens JM-1 (IAA generation and solubilization phosphate and Zn) also aided in the enhancement of maize growth indices.
Given the importance of microorganisms in nutrient mineralization and solubilization, soil organic matter creation, and pathogen pressure, rhizosphere engineering would benefit from methodologies and tools that permit us to modify the microbiome (Wallenstein, 2017). The interaction between plants and rhizospheric bacteria has been thoroughly investigated for biogeochemical cycling activities, plant growth promotion, and biocontrol, all of which are critical for plant health. Hence the need for in-depth knowledge of microbial diversities in the plant rhizosphere to enable adequate deployment of plant beneficial microbes toward plant growth promotion (Olanrewaju et al., 2019). Variations in the physical environmental condition and structure of the host-associated rhizosphere microorganisms are frequently linked to plant pathogen invasion. Thus, understanding plant-pathogen infections in highly varied field conditions constitutes a critical challenge for food security and crop protection in the future (Wei et al., 2018). The pathogen's introduction has the potential to disrupt the plant's finely regulated relationships with its microbiome. Changes in the native microbial community structure and interactions that provide favorable conditions for the pathogen virulence led to fast declines in host health and productivity (Zhang et al., 2021). For that reason, the pathogen must compete with other bacterial species for colonization of the plant rhizosphere, which is the initial stage in infection. When a pathogen reaches a certain density, it activates its virulence genes and invades plant roots (Wei et al., 2018), which may infect host tissue and successfully exit the rhizosphere war zone, most soil-borne pathogens must grow saprophytically in the rhizosphere to influence their host or to attain adequate numbers on their host. The microbial population of the soil in which infection occurs has an impact on the pathogen's success. To some extent, typical agricultural soils have the ability to restrict a pathogen. This can be determined by comparing the severity of disease after pathogen inoculation in sterilized and non-sterilized soils (Berendsen et al., 2012). Recent research has found that microbiome functioning, including disease resistance, may result through the interaction of species instead of the existence of a specific feature or species. This have been shown as an emerging approach to overcoming the laboratory to field hurdles, since the use of microbial consortia entails the deployment of microbes with similar mode of action that are able to tolerate different environmental conditions and effective om the plant genotypes, thereby complementing each other. This has been effectively explored in tomato, maize and potato among other crops (Compant et al., 2019). Each stage of ecological succession is connected with certain features in the main species, putting the existing community arrangement in the context of a dynamic temporal procedure. When applied to the rhizosphere, ecological succession can offer a novel prognostic outline for species and trait occurrence, offer new entry points to engineer its ability to prevent diseases, and elucidate how a suppressive microbiome assembles (Hu et al., 2020).
The plant-soil feedback: Essential tools in microbiome management
The past investigations of plant-soil feedback have revealed the varying effect of different plant species on the biotic and abiotic soil conditions, which in turn affects the growths of other heterospecific and conspecific individuals in that soil (Kulmatiski and Kardol, 2008). Either positively or negatively, the plant-soil feedbacks can drive patterns of plant diversity, succession, and invasion, which can shape the community composition and ecosystem functioning. While the environmental forces that occur over the landscape include stress, disturbance, and competition, plants allocate resources to growth, reproduction, and maintenance in diverse ways to cope with these constraints (Beals et al., 2020).
One of the basic structures that allow plant stability against both biotic and abiotic pressures is the root system. Although scientists have given less attention to the study of plants root, roots have been found essential for plant productivity and adaptations. The root architecture is made up of structural features such as root length, length of lateral roots, and spread number that enable plants to exhibit plasticity in response to environmental changes, and the optimum performance of the root (Khan et al., 2016). This three-dimensional spatial organization of root structures is especially important for the function of roots in difficult situations. A deep root structure, for example, is required for plants to use water and nitrate in deeper soil layers, and hence useful for drought resistance, mostly in nitrogen-scarce circumstances. A shallow root structure with increased adventitious roots to promote foraging on the topsoil, on the other hand, is critical for crops to acquire comparatively steady nutrients like phosphorus. Developing cultivars with root architectures that are appropriate for the field conditions promises to be a long-term and cost-effective way to improve crop nutrient efficiency and stress tolerance (Yang et al., 2017). The advent of more detailed molecular and analytical tools which allow full explanation of the dynamics of rhizosphere and endosphere communities has sparked transformed interest in plant-microbe interactions.
Recent data has shown that root type and location influence the composition and diversity of the communities of bacterial, fungal, and actinobacterial, including specialized functional groups like arbuscular mycorrhizal fungi, across a wide range of plant species. Differences in root assembly and the quantity and composition of root exudates, as well as plant-microbe, microbe-microbe, and microbe–fauna interactions, all contribute to these variances (Richardson et al., 2021). The importance of interactions between plants and their phyllosphere microbes is gaining attention, as they stimulate plant development and contribute to pathogen defense, these may later alter the suitability of natural plant inhabitants along with the quality and production of agricultural products. Meanwhile, endophytic bacteria have been recognized for their ability to defend their hosts from pests, insects, and microbiological diseases, thereby acting as biocontrol agents (Fausto et al., 2018). Crop rotation may also improve microbial diversity in soil because various plant species favor distinct bacteria in the soil due to changes in root exudation. Intercropping, where diverse crops are planted together and the roots of different plant species interact directly, has a good impact on soil fertility in addition to microbial variety and activity (Mitter et al., 2019).
A greater understanding of the root microbiome succession, such as how the microbes vary in response to crop development, opens up new-fangled possibilities for reaping the advantages of beneficial root–microbial interactions (Richardson et al., 2021). Metagenomics has a large potential to equip with vital information on plant-microbe interactions, which is required for new technologies to boost agricultural output in the long run (Bramhachari et al., 2017).
Soil microbial communities play a contributory role in determining plant growth and soil fertility. The changes that occur in their structure and dynamics in response to various soil management approaches can provide information regarding soil quality and biological complexity (Fausto et al., 2018). Also, microbes such as Azotobacter spp., Azoarcus spp., Burkholderia sp., Actinorhizobium spp., Rhizobium spp., Gluconacetobacter sp., Herbaspirillum sp., Bacillus polymyxa, and especially Azospirillum sp., Enterobacter, and Pseudomonas spp. that stimulate nutrient acquisition and plant growth have traditionally been utilized in agriculture as single strains to counter nitrogen and phosphorus fertilizer inputs Thus, a variety of parameters, including tissue, genotype, physiological status, growth stage, soil ecological conditions, and agricultural practices influence the plant microbial colonization. Natural population studies, on the other hand, reveal that clusters of bacteria with specific functions play crucial roles in adhering and releasing inorganic nutrients to physical surfaces, along with breaking down organic wastes and integrating them into the soil (Backer et al., 2018; Arif et al., 2020; Ray et al., 2020). Soil microbes are regarded as a significant constituent of the complex interplay of elements that contribute to the environmental quality required for long-term, healthy food production (Barea, 2015).
Soil organic matter stabilization, decomposition, bioremediation, nutrient cycling, and soil aggregate production are all significant tasks carried out by soil microorganisms. This reaction with organic matter and inorganic fertilizers consequently determine the fitness of soil health for crop production (Dangi et al., 2020). Furthermore, plant beneficial microbes are essential in the development of plant growth stimulators, bio-pesticides, and bio-fertilizers to decrease agrochemical use. These microbes improve soil fertility, soil health, and plant growth in a variety of ways, including improving nutrition (recycling, nutrient mobilization, nitrogen fixation), regulating phytohormone levels (cytokinins, gibberellic acid, ethylene, and indole acetic acid, among others), suppressing soil-borne pathogens (via antibiotic production, cyanides, and siderophores), and environmental symbiosis (via siderophores). Microbes may improve environmental conditions and soil biochemicals, while generating plant tolerance to environmental challenges, as a result of these qualities (Sahib et al., 2020). Organic fertilizers have been proven to recover soil microbial biomass by providing carbon-rich chemicals to the normally carbon-limited microbial populations in agricultural soils. Change of practices in soil management, for example, organic fertilizer treatment, has been found to increase biochemical properties and soil microbial quickly after application. Although there are benefits to employing organic nitrogen in traditional farming where mineral manures are widely employed, this area has been scarcely investigated (Dangi et al., 2020). Breeding for increased plant response for enhanced interactions and colonization of the plant environment is a crucial feature for the more efficient and effective use of microorganisms in agriculture. Plant breeding has mostly focused on increasing harvest yield and developing pathogen resistance; however, these procedures have brought about a decrease in genetic diversity in modern crops (Mitter et al., 2019).
Interplay of the environment and species-specific microbiome on plant health
The potential of some soil microbes to promote plants' health and performance has been harnessed to boost pest management and agricultural yield by altering the soil microbiomes community (Howard et al., 2020). Since the era of next-generation sequencing, a renewed interest has sparked in the composition and role of microbial species diversity toward controlling plant productivity and soil health in broader ecological contexts (Sahib et al., 2020). As a result, a wide range of bacteria, fungi, and archaea components of the soil microbiome have received significantly greater attention in soil microbiology research (Barea, 2015). In line with some earlier studies, plant species in different successional phases possess different ecophysiological properties that could significantly impact the soil biological features, as in the case during early succession when fast-growing plant species produce a labile carbon substrate that favors bacterial-dominated communities. On the other hand, slow-growing plant species that control late-successional phases produce complex substrates (high in lignin) which favor the efficient lignin decomposing fungi (Shanmugam and Kingery, 2018). There is growing knowledge of the interactions between any consortium or inoculant strain and the receiving environment, such as abiotic soil conditions, the target plant and soil, their associated micro-and macrobiota, and more broadly ecological conditions that provide knowledge-based approaches for microbiome applications toward developing more targeted and-effective microbial applications (Mitter et al., 2019) (Figure 1).
Figure 1
Plant-associated microbiomes can benefit their hosts, however, the rhizosphere's microbial makeup, along with colonization efficiency, are influenced by factors such as ecological, host's genetics, and physiological status (Rodriguez et al., 2019). To a greater extent, plant properties including biomass production, disease suppression, growth response, and flowering phenotype are all linked to specific plant microbiota. As a result, plant microbiota modification or the effects of farming management will influence plant characteristics and performance (Compant et al., 2019). The functional and mechanistic elements of the interactions between microorganisms, plants, the environment, and agricultural management methods are essential to realizing the predicted benefits of plant microbes in agriculture (Busby et al., 2017) (Figure 1).
Mechanism of action of beneficial microbes
Microbial biological control agents work in a variety of ways to protect crops against diseases. The many processes used by bio control agents to control plant diseases can be broadly characterized as direct antagonisms and Indirect antagonism.
Direct antagonism
Physical contact and/or a high degree of selectivity for infections by the bio control agent cause direct antagonism. It contains the following items:
a) Hyperparasitism—this interaction entails the tropic development of a biocontrol agent toward the target organism, coiling, and eventual attack and disintegration of the target pathogen's cell wall or membrane by enzyme activity. Fungi frequently engage in this type of interaction, e.g., Trichoderma (Junaid et al., 2013; Köhl et al., 2019a,b).
b) Direct Antibiosis—Antimicrobial metabolites are secondary metabolites that belong to a diverse category of organic, low-molecular-weight chemicals produced by bacteria and are toxic to other microorganisms' growth or metabolic processes (Köhl et al., 2019b). However, because of the modest quantities produced in comparison to other, less hazardous organic chemicals in the phytosphere, the effective quantities are difficult to quantify. A bio control agent that produces adequate amounts of antibiotics in the area of the plant pathogen is effective (Junaid et al., 2013). Biocontrol bacteria from the genera Agrobacterium, Bacillus, Pantoea, Pseudomonas, Serratia, Stenotrophomonas, Streptomyces, and others have been found to produce antimicrobial compounds, most of which have broad-spectrum activity (Köhl et al., 2019b).
Indirect antagonism
The capacity of biocontrol bacteria to boost plant development indirectly has piqued attention, in terms of getting a better understanding of some of the underlying mechanisms used by biocontrol bacteria and commercializing these bacteria instead of chemical pesticides (Admassie et al., 2020). It includes the following:
a) Competition—Soils and living plant surfaces are frequently nutrient-limited environments from a microbiological standpoint. As a result, a microorganism colonizing the phytosphere must efficiently compete for the available nutrients. Both biocontrol agents and infections battle for nutrients and space in the environment in order to develop themselves. This rivalry is thought to be an indirect interaction between the pathogen and the biocontrol agent, in which the pathogens are kept out of the site by depletion of the food supply and physical occupation (Junaid et al., 2013). For example, Bacillus spp. can control fungal pathogens by competition for space at the root surface and nutrients, particularly those produced as seed or root exudates, occurring in the rhizosphere (Pertot et al., 2015).
b) Induced Resistance and Priming—Plants defend themselves against infections through a number of physical and chemical processes. One of the most promising agronomic strategies for preventing biotic losses in crops is to improve resistance. Inducible resistance mechanisms supplement constitutive mechanisms like cuticles. Stimuli identified by particular recognition receptors activate induced plant defense mechanisms. MAMPs are microorganism-produced resistance-inducing stimuli. MAMPs with recognized receptors include glucan, chitin, and xylan, which are generated by Phytophthora megasperma and Trichoderma viride, respectively (Köhl et al., 2019b).
Bioprospecting rhizospheric microorganisms as biocontrol agents
Microbial-based solutions are currently one of the rapidly-growing agricultural sectors which are potential alternatives or complement the use of synthetic fertilizers and pesticides (Malusà et al., 2021). Microbial pesticides are biopesticides created from beneficial microorganisms that promote plant development, and nutrient utilization efficiency which results in higher agricultural yields (Asad, 2022). Furthermore, microbial pesticides have the potential to suppress pests and are one of the choice alternatives for plant disease management in recent times (Patil and Solanki, 2016). Since only about 1% of the candidate isolates retrieved from the studied samples could eventually become commercial products, many scientists currently explore approaches to improve the search and identification of suitable microbial strain that qualifies as potential biopesticides. However, recent approaches have embraced the use of DNA sequencing of representative samples to directly target activity-related genes (Glare et al., 2016). This method has been promising in unveiling the diversities of microbes associated with the rhizosphere for possible exploration of those with biocontrol functions. Hence, discovering, screening, identifying, and characterization of microorganisms with biocontrol potentials and the ability to colonize, persist, and adapt to a complex environment like the rhizosphere is an intriguing disease management method (Gomez-Lama Cabanas et al., 2018) (Figure 2). Identification and selection of a suitable sampling environment where prospective microbial candidates could be isolated is the first step in the development of microbial-based biopesticides. It is important to assess the biology and nature of the prevailing pest problem in the area where a microbial biopesticide is planned to be used.
Figure 2
This assessment considers the biological principles of diseases and pests such as the host range, nature of the symptoms, the most vulnerable phases of the host, and the most suitable period of intervention (Mandakini and Manamgoda, 2021). Isolation using culture-dependent approaches have traditionally been used to exploit ambient microbiomes. High-throughput sequencing techniques that have been developed in recent decades have shown considerable promise in probing the intricate microbial networks found in plant microbiomes. The efficacy of the sequencing method in the identification of new and highly efficient microbial strains has been proved (Malusà et al., 2021).
Microorganisms exert biocontrol influence through a variety of processes, including antibiosis, parasitism, competition, and generation of plant systemic resistance. These properties promote the employment of biocontrol bioassays in screening for members with biopesticide potentials among a large number of microbial (Mandakini and Manamgoda, 2021). Microbiome modification has also recently been revealed as an effective method for screening microbial strains (Malusà et al., 2021), while the incorporation of molecular approaches into the screening process has also been equally beneficial in determining the full potential of the promising strains.
Formulation and application of microbial biopesticides
The first and most important step in the formulation of biocontrol agents is biomass generation. Culturing conditions affect the fitness and viability of microorganisms throughout formulation, storage period, application, as well as population densities upon harvest. A procedure that is peculiar to each microbial strain must be properly screened to enhance the performance of microbes as bioagents in the field (Bejarano and Puopolo, 2020). Once the biopesticide inoculum is generated, it must be kept stable during storage, distribution, and use at the target site. The formulation enables technical product stability, as well as persistence, safety, high efficacy, and user-friendliness. As a result, it is regarded as an important stage in the development of a high-quality and practical biopesticide. The active component (generated inoculum) is blended with inert ingredients like transporters, surface active ingredients (stickers, spreaders), and other additives during the formulation process (stabilizers, coloring agents, etc.) (Bejarano and Puopolo, 2020).
Biopesticides formulation becomes more efficient as production technology improves in the last few decades, this has therefore resulted in some breakthroughs recorded in the field of biopesticides. In the recent times, the application, persistence, and efficacy of biopesticides are enhanced with the use of prills and emulsions in its formulation. More so, the application through seed coating is appreciated for its appealing means of delivering biopesticides particularly in the soil. This method increasingly gains relevance as more agents are discovered to be rhizosphere colonizers or even capable of endophytic colonization (Glare et al., 2016). However, one of the difficult aspects of biopesticides use is that most application procedures were designed for synthetic pesticides rather than living organisms. Whereas, to ascertain the efficacy of the formulation produced, it must be successfully delivered to the target plant diseases under a favorable field conditions suitable for the disease expression (Mishra et al., 2019). Since the application should ideally bring the active chemicals in contact with the pest/disease and keeping them active for several weeks. The aboveground application has traditionally been carried out with spray applicators, while the below ground application of microbial agents with the use of specialized equipment with appropriate droplet size, and focused treatment, are receiving more attention (Glare et al., 2016). Although, the roles of biological formulations as biofertilizer which entails the improvement of resource acquisition and efficient use, and biopesticide which reducing losses due to pests and pathogens, has been embraced by the legislation and regulatory agencies (Malusà et al., 2021). However, the current legislative framework in place in many countries as regards the development and marketing of microbial-based goods makes it difficult to vigorously explore and take advantage of the multifunctionality of these beneficial microbes.
The beneficial microbes and soil health: Impacts on food safety
Soil health refers to the ability of soil to continue to operate as a vital living ecosystem that supports humans, animals, and plants, and it links agricultural and soil research to stakeholder demands, policy, and long-term supply chain management. Historically, soil assessments were focused on crop production (Lehmann et al., 2020), but existing safe agricultural practices emphasize the decrease of agrochemical usage in favor of different forms of eco-friendly crop management, like the use of abiotic and biotic stress-tolerant rootstocks or the improvement of productivity and plant health through soil management (Vida et al., 2020). Furthermore, the biotic stressors which consist of the fungal pathogens of maize such as Exerohillum turcicum causing Northern corn leaf blight (NCLB), Bipolaris maydis (Southern corn leaf blight) Rhizoctonia solani (Banded leaf and sheath blight), Colletotrichum graminicola (Colletotrichum graminicola) and Macrophomina phaseolina (Charcoal rot). Also, the bacteria diseases caused by the pathogens Dickeya zeae (Bacterial stalk rot), Clavibacter nebraskensis (Goss's bacterial wilt and blight), Xanthomonas vasicola (Bacterial leaf streak/spot) among many others reduce the grain quality and yield produced (Damicone et al., 2018; Begum et al., 2019; Zhu et al., 2021) (Table 1).
Table 1
| Fungal pathogens | Hosts | Disease caused | Antimicrobial and growth-promoting microbes | References |
|---|---|---|---|---|
| Exerohillum turcicum (Teleomorph Setosphaeria turcica), Helminthosporium turcicum (Pass.), Drechslera turcica (Pass.) Subramanian and Jain, Xanthomonas axonopodis pv. coracanae | Maize, Sorghum, Millet | Northern Corn Leaf Blight (NCLB) | Rhizophagus intraradices | Begum et al., 2019; Ogolla et al., 2019; Degani et al., 2020; Zhu et al., 2021 |
| Bipolaris maydis (Teleomorph Cochliobolus heterostrophus) | Maize | Southern corn leaf blight (SCLB) | Bacillus subtilis, Fenneliformis mossease | Begum et al., 2019; Zhu et al., 2021 |
| Rhizoctonia solani (Teleomorph Thanatephorus cucumeris) | Maize, Soybean | Banded leaf and sheath blight (BLSB) | Pseudomonas aeruginosa, Trichoderma, Gliocladium, Pseudomonas, Bacillus subtilis, Paenibacillus polymyxa, P. fluorescens, Chryseobacterium gleum, Streptomyces spp., Binucleate Rhizoctonia spp. and hypovirulent R. solani | Herr, 1995; Fiers et al., 2012; Ajayi-Oyetunde and Bradley, 2018; Rai and Singh, 2018; Begum et al., 2019; Singh et al., 2020 |
| Cercospora zeina, Cercospora zeae-maydis, Curvularia lunata (Teleomorph Cochliobolus lunata) | Urdbean or Black gram (Vigna Mungo L.), Arachis hypogea, Vigna sinensi, Pennisetum typhoides, Vigna rediata, Glycene max, Vigna mungo, Oryza sativa, Zea mays | Gray leaf spot (GLS)/Curvularia leaf spot (CLS) | Bacillus subtilis | Lal et al., 2013; Xie et al., 2020; Zhu et al., 2021 |
| Colletotrichum graminicola (teleomorph Glomerella graminicola) | Maize, wheat, sorghum, bluegrass, barley, ryegrass | Anthracnose stalk rot, Anthracnose leaf blight | Streptomyces ganmycicus, Sporobolomyces roseus | Elizabeth and Mordue, 1967; Back et al., 1999; Zhu et al., 2021 |
| Puccinia polysora | Maize | Southern rust | Trichoderma spp. | Veenstra et al., 2019; Zhu et al., 2021 |
| Fusarium verticillioides, Fusarium graminearum (Teleomorph Gibberella zeae), Aspergillus flavus, Stenocarpella maydis | Maize, wheat (Tricitcum aestivum & Tricitum durum), Oat (Avena sativa), Barley (Hordeum vulgare) | Maize ear and stalk rot, Fusarium head blight | Trichoderma asperellum, Bacillus velezensis, Bacillus subtilis, Trichoderma harzianum, Trichoderma viride, Pseudomonas fluorescens | Ye et al., 2012; Ramesha, 2018; Arici and Tuncel, 2020; Tom and Patel, 2021; Zhu et al., 2021 |
| Macrophomina phaseolina | Sunflower, Medicago littoralis, Vigna mungo, Lens culinaris, maize, and Medicago scutellata | Charcoal rot | Pseudomonas spp., Trichoderma | Ali and Dennis, 1992; Al-Sa'di et al., 2008; Emayavarman et al., 2019; Degani et al., 2020; Xavier and Kaushik, 2021 |
| Pythium aphanidermatum and Pythium inflatum | Pawpaw, Cucumber, Soybean, pepper, cotton, cucurbits, turf-grasses, beets, and chrysanthemum | Pythium stalk rot | Bacillus subtilis, Streptomyces spp. | Olawuyi et al., 2014; Abd-Elsalam, 2020; Hassanisaadi et al., 2021; Zhu et al., 2021 |
| Bacteria pathogens | ||||
| Dickeya zeae (Syns. Erwinia chrysanthemi pv. Zeae) | Maize, rice, banana | Bacterial stalk rot, soft rot, footrot | Pseudomonas aureofaciens, P. chlororaphis, P. putida, P. fluorescens, P. kilonensis, P. Protegens | Hu et al., 2018; Begum et al., 2019; dos Santos et al., 2020; Zhu et al., 2021 |
| Clavibacter michiganensis subsp. Nebraskensis | Maize, Sorghum (Sorghum halepense), Large Crabgrass (Digitaria sanguinalis), Ryegrass (Lolium multiflorum) | Goss's bacterial wilt and blight | Pseudomonas sp., Bacillus sp. | Ikley et al., 2015; Goyal and Anvitha, 2021; Zhu et al., 2021 |
| Xanthomonas vasicola pv. vasculorum (Xvv), Xanthomonas campestris | Maize, Banana, Sorghum, sugarcane | Bacterial leaf streak, bacterial leaf spot | Rhizobium, Azotobacter, Azospirillum | Coutinho et al., 2015; Lalitha, 2017; Damicone et al., 2018; Ocimati et al., 2018 |
| Pantoea stewartii subsp. stewartii (Pss), Pantoea ananatis, Erwinia amylovora | Maize, Onion, Apple (Malus domestica), Bermuda grass, soybean, cowpea | Stewart's wilt, Fire blight, die-back, leaf blotches and spots, stalk, fruit, and bulb rot. | Goszczynska et al., 2007; Baek et al., 2018; Stumpf et al., 2018 | |
Fungal and bacteria pathogens, diseases caused, and biological agents for managing agricultural crops.
Recent research has shown that using a beneficial microbe can improve agricultural output and plant health when produced under constrained environments. Varying antimicrobial and growth-promoting microorganisms have been investigated and developed from beneficial microbes such as Pseudomonas aureofaciens, Pseudomonas chlororaphis Bacillus sp., Rhizobium, Azotobacter, and Azospirillum among several others, and were effective in mitigating the debilitating effect of the pathogens (Lalitha, 2017; Begum et al., 2019; dos Santos et al., 2020) (Table 1).
The diversity of microorganisms in the rhizosphere zone aids plant growth by providing defense against pests and pathogens, facilitating nutrition uptake, and assisting plant tolerance to a variety of abiotic and biotic stimuli. Various types of abiotic stress include salinity, high temperature, and drought which results in negative impacts, for example, losses in crop productivity by disease susceptibility, nutrient acquisition, reducing water absorption and disturbing hormonal balance, and by affecting the photosynthetic capacity of the plant. However, because only around 1–5% of the bacteria on the planet are cultivable, the remaining 95–99% of germs are uncultivable; these helpful microbes are not fully utilized. For numerous years, understanding plant-microbe interactions have been a major emphasis of study (Kumar and Dubey, 2020). The employment of beneficial microorganisms (which improve the plant's health and quality, as well as assist in the reprocessing of crop leftovers with less ecological impact) is one of the most important techniques for long-term energy and food production (Dubey et al., 2019). Numerous soil microorganisms interact with each other and with plants in a variety of ways that aid in the maintenance and molding of various ecosystem components.
Healthy soils are the base of productive and sustainable agroecosystems, and they can be maintained by following basic soil health principles such as increasing plant diversity through crop rotation, protecting surface soils by growing more plants, minimal soil disturbance, polycultures, and cover crops, and enhancing soil microbiome, among others. Microbes aid to maintain soil health, improving root growth, water retention capacity, vital nutrient availability, carbon storage, cycling, filter contaminants, and conserving biodiversity (Dubey et al., 2019).
Beneficial microbes are opening up new avenues for long-term disease (pathogen) control, emphasizing the relevance of the plant microbes for crop productivity (Bonanomi et al., 2018). Since the 1980s, organic amendments have been used to manipulate the soil microbiota to minimize pathogen inoculum or virulence in favorable soil, albeit the efficiency of these methods varies depending on the pathogen/host system (De Corato, 2020). Compost, crop residues, peat, organic wastes, and biochar are examples of such organic soil additives (Akanmu et al., 2020; Chukwuka et al., 2020), although biofumigation is also used, for example, to reduce disease through soil fungistatic (Bonanomi et al., 2018). Organic manure (both animal dung and biomass) applied as a soil amendment, in contrast to issues linked with the use of agrochemicals, plays a vital role in the control of plant health and the recycling of soil nutrients (Akanmu et al., 2021). Organically altered soil has a potentially superior operational microbiome, with more positive microbial activities and functionally connected species than soils that have been fertilized with chemical fertilizers.
To better understand soil health, it will be required to characterize the functional groupings of microorganisms that are connected with specific organic amendments. Organic amendments including materials produced from composts, farmyard manure, crop residue and biochar among others, have been reported to modify soil structure and enables the efficient absorption and both nutrient and water retention in the soil (Akanmu et al., 2021). Organic amendments fine-tuned and optimized for specific soil/crop combinations, would create long-term microbial ecosystem services and soil health, resulting in yields that are equivalent to or greater than chemical fertilizers alone (Arif et al., 2020). Since the early 2000s, supplementing beneficial external microbiota with Composts, organic amendments, and biological control agents has appeared to be a potential strategy for boosting the suppression of favorable soils (De Corato, 2020). As a result, soil organic matter can be conserved with the help of organic amendments in agricultural systems, which is a recognized technique for reducing soil deterioration. Organic additions, on the other hand, have the potential to change the soil microbiome. The quantity and quality of organic matter input not only affect the soil's physicochemical properties, but also affects biotic factors related to the soil microbiota, such as microbial biomass and diversity, community structure, and soil activities, all of which have a direct impact on disease biological control (Vida et al., 2020).
Plants contribute to the stability of the rhizobiome by producing fixed carbon resources. Plant beneficial microbes, in turn, aid plants' growth by root modification, acquiring nutrients and protecting plants from infections, among other things. As a result, the rhizobiome plays a crucial role in sustaining the plant's health. Disassembling plant microbiomes and building synthetic microbial communities for reconstitution studies to examine interspecies and intraspecies interactions is a potential way to understand the reciprocal impacts of plants and their microbiota (Lucaciu et al., 2019). Fast-growing species were gradually substituted by stress-tolerant and hostile species as the plants grow. Using synthetic consortia derived from different plant growth phases shows that the high functional diversity of climax microbiomes contributes to increased resistance to pathogenic microbial invasion. Hence, root-associated microbes have the potential of improving plant efficiency and output in cropping systems, according to a growing body of studies (Ab-Rahman et al., 2018; Hu et al., 2020).
Current trends in the use of rhizospheric microorganisms
The use of rhizospheric microbes has been explored in the formulation of biopesticides, and the efficacy of the products against pest and diseases in a diverse type of crops have been proved. Newly discovered microbial species and strains are analyzed on a regular basis for their potential to serve as a biocontrol agent. Despite several typical drawbacks, the use of biocontrol agents still holds a lot of potential (Köhl et al., 2019a). In recent times, many biopesticide companies are entering into licensing agreements to market and sell microbial biocontrol products, while many international companies have ventured into the formulation and marketing of microbial biocontrol products (Marian and Shimizu, 2019). However, despite the large corpus of research on the bioagents' ability to protect crops, only a few microbes are recognized as active substances at the time of writing, and the majority of which are Trichoderma and Bacillus spp. strains (Table 2).
Table 2
| S/N | Trade name and company | Type | Microorganism | References |
|---|---|---|---|---|
| 1 | AQ 10 WG—CBC EUROPE | Fungicides | Ampelomyces quisqualis AQ10a | Benuzzi and Baldoni, 2000; Pertot et al., 2015 |
| 2 | Blossom-Protect® | Bactericides and fungicides | Aureobasidium pullulans DSM 14940 and DSM 14941 | Chen et al., 2009; Freimoser et al., 2019; Sellitto et al., 2021 |
| 3 | Serenade ASO—Bayer CropScience | Bactericides and fungicides | Bacillus amyloliquefaciens QST 713 | Chen et al., 2009; Matzen et al., 2019; Bejarano and Puopolo, 2020 |
| 4 | Basf—Serifel, Histick N/T, Integral, Subtilex | Fungicides | Bacillus amyloliquefaciens MBI 600 | Dimopoulou et al., 2021; Samaras et al., 2021a,b |
| 5 | FZB24—AbiTEP, Novozymes | Fungicides | Bacillus amyloliquefaciens FZB24 | Gül et al., 2008; Chowdhury et al., 2015; Pertot et al., 2015; Bejarano and Puopolo, 2020; Dimopoulou et al., 2021 |
| 6 | Amylo-X; CBC Europe S.r.l.- Biogard Division, Nova Milanese (MB), Italy & Certis USA L.L.C | Fungicides | Bacillus amyloliquefaciens subsp. plantarum D747 | European Food Safety Authority, 2014; Pertot et al., 2015; Rotolo et al., 2016; Bejarano and Puopolo, 2020; Dimopoulou et al., 2021 |
| 7 | VOTiVO®–(Bayer CropScience) | Nematicides | Bacillus firmus I-1582 | Pertot et al., 2015; Mendis et al., 2018; d'Errico et al., 2019; Bejarano and Puopolo, 2020; Ghahremani et al., 2020 |
| 8 | GB34 Concentrate Biological Fungicide—Bayer Crop Science | Fungicides | Bacillus pumilus QST 2808 | Pertot et al., 2015; Wang et al., 2015; Lazzari et al., 2018; Dimopoulou et al., 2021 |
| 9 | Avogreen—Next | Fungicides | Candida oleophila O | Lahlali et al., 2011; Pertot et al., 2015; Bejarano and Puopolo, 2020 |
| 10 | Prestop—Biobest | Fungicides | Clonostachys rosea J1446 | Chatterton and Punja, 2010; Gimeno et al., 2019; Bejarano and Puopolo, 2020 |
| 11 | Contans WG—Bayer CropScience | Fungicides | Coniothyrium minitans CON/M/91-08 (DSM 9660) | Pertot et al., 2015; European Food Safety Authority, 2016; Bejarano and Puopolo, 2020 |
| 12 | MeloCon WG | Nematicides | Paecilomyces lilacinus 251 | Kiewnick and Sikora, 2006; Pertot et al., 2015; Dahlin et al., 2019; Bejarano and Puopolo, 2020 |
| 13 | Cerall—BioAgri | Fungicides | Pseudomonas chlororaphis MA342 | Pertot et al., 2015; Anderson et al., 2018; Bejarano and Puopolo, 2020; Products et al., 2020 |
| 14 | Proradix®–Sourcon Padena | Fungicides | Pseudomonas sp. DSMZ 13134 | Buddrus-Schiemann et al., 2010; Pertot et al., 2015; Pellicciaro et al., 2021 |
| 15 | Biopreparáty, Ltd (Únětice, Czech Republic) | Fungicides | Pythium oligandrum M1 | Pertot et al., 2015; Gabrielová et al., 2018; Bejarano and Puopolo, 2020; Pisarčik et al., 2021 |
| 16 | Mycostop—Vedera Oy | Fungicides | Streptomyces griseoviridis K61 | Pertot et al., 2015; Bejarano and Puopolo, 2020 |
| 17 | Actinovate AG—Novozymes | Bactericides and fungicides | Streptomyces lydicus WYEC 108 | Chen et al., 2016; Evangelista-Martínez et al., 2020; Dimopoulou et al., 2021 |
| 18 | Remedier WP | Fungicides | Trichoderma asperellum ICC012, T25 and TV1 | Woo et al., 2014; Pertot et al., 2015; Bejarano and Puopolo, 2020 |
| 19 | T34 biocontrol—Asperello Biobest, Biocontrol Technologies S.L., Biolchim | Fungicides | Trichoderma asperellum T34 | Pertot et al., 2015; Bejarano and Puopolo, 2020; Estévez-Geffriaud et al., 2020; Gugliuzzo et al., 2022 |
| 20 | Binab T—Bio-innovation AB | Fungicides | Trichoderma atroviride IMI 206040 and T11 | European Food Safety Authority, 2015; Pertot et al., 2015; Morán-Diez et al., 2019; Bejarano and Puopolo, 2020 |
| 21 | Tri-Soil®, Esquive WP—(Agrauxine) | Fungicides | Trichoderma atroviride I-1237 | Woo et al., 2014; Letousey et al., 2017; Mounier et al., 2017 |
| 22 | VINTEC (Bi-Pa NV/SA, Belchim crop protection Italia) | Fungicides | Trichoderma atroviride SC1 | Savazzini et al., 2009; Bejarano and Puopolo, 2020; Gugliuzzo et al., 2022 |
| 23 | Remedier WP (Isagro USA) | Fungicides | Trichoderma gamsii ICC080 | Woo et al., 2014; Pertot et al., 2015; Bejarano and Puopolo, 2020; Celar and Kos, 2022 |
| 24 | TRIANUM-P (Koppert B.V., Koppert Italia), Agroguard WG™ Antagon WP™ ECO-T™, PlantShield™/RootShield™, Trichosav | Fungicides | Trichoderma harzianum T-22 and ITEM 908 | Pertot et al., 2015; Gugliuzzo et al., 2022; Shahriar et al., 2022 |
| 25 | Binab T—Bio-innovation AB | Fungicides | Trichoderma polysporum IMI 206039 | European Food Safety Authority, 2013; Pertot et al., 2015; Bejarano and Puopolo, 2020 |
Commercialized microbial biocontrol formulations.
Conclusion and future prospects
Effective management of plant health is strategic to attaining sustainable food production and reducing hunger, thereby fulfilling an important Sustainable Development Goal (SDG) of 2030. To achieve this, an efficient disease and pest management approach focused on disease prevention need to be instituted. This could be achieved through the beneficial microbes' roles in the abatement of pathogenic invasion, support of plant-soil feedback, and modulating the species-specific rhizosphere microbiome interplay toward plants' wellness and productivity. Hence, the gateway to attaining safe and sustainable plant health is dependent on the efficient coordination of the rhizosphere microbiome in plant development and disease management, as well as their sustainable deployment as biofertilizers and biopesticides in managing plant health. Of recent. the breakthroughs in system biology, molecular biology, and associated computational technologies has enabled the eludication of the structural and functional characteristics of microorganisms with prospects in growth promotion and biocontrol potientials. This has therefore enabled the indepth understanding of the rhizospheric microbes, however, the functional dynamics among the antagonists opens up new possibilities for the design of microbial antagonist consortia which could be an effective broad spectrum microbial formulation against varying plant diseases. Although strain mixtures for the biocontrol of plant pathogens are already commercially available as described in the literature, employing taxonomically divergent but functionally complementary strains could be a promising approach to follow in the near future in the quest to design a standardized, multi-targeted, efficacious biocontrol strategy.
Funding
OB recognizes National Research Fund (NRF South Africa) for grants (UID123634 and UID132595) that support work in her research group.
Publisher's note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
Statements
Author contributions
All authors listed have made a substantial, direct, and intellectual contribution to the work and approved it for publication.
Acknowledgments
SD and AA appreciate the North-West University, South Africa for the respective Postgraduate and Postdoctoral privileges enjoyed in the University.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
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Summary
Keywords
microbial community, food security, food safety, plant-soil-microbe association, rhizosphere engineering, plant disease management
Citation
Dlamini SP, Akanmu AO and Babalola OO (2022) Rhizospheric microorganisms: The gateway to a sustainable plant health. Front. Sustain. Food Syst. 6:925802. doi: 10.3389/fsufs.2022.925802
Received
21 April 2022
Accepted
07 July 2022
Published
04 August 2022
Volume
6 - 2022
Edited by
Vineet Kumar, Lovely Professional University, India
Reviewed by
Jamilah Syafawati Yaacob, University of Malaya, Malaysia; Ezekiel Mugendi Njeru, Kenyatta University, Kenya
Updates
Copyright
© 2022 Dlamini, Akanmu and Babalola.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Olubukola Oluranti Babalola olubukola.babalola@nwu.ac.za
This article was submitted to Crop Biology and Sustainability, a section of the journal Frontiers in Sustainable Food Systems
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