Production of Trichoderma Biofertilizer from Agro-waste for Eco-sustainable Agriculture

Production of Trichoderma Biofertilizer from Agro-waste for Eco-sustainable Agriculture

Published: 2025.09.26
Accepted: 2025.09.19
14
Institute of Agriculture and Life Sciences, Gyeongsang National University, Jinju, 660-701, South Korea
Professor
Department of Environment, Life and Chemistry Gyeongsang National University, Korea

DOI: https://doi.org/10.56669/MMRA3791

ABSTRACT

Trichoderma is widely used in agriculture due to its known biocontrol mechanisms. By colonizing plants, either as an endophyte or on their roots, Trichoderma has developed the ability to interact with the plants and provide a variety of benefits to its hosts. The complexity of this plant-microbe association has led to a great deal of interest in the study of Trichoderma, ranging from its ability to act as a plant growth promoter to its ability to activate plant defense mechanisms against biotic and abiotic stresses. This review discusses the ideal properties of Trichoderma. It highlights its potential in biocontrol of plant diseases and pests, enhancement of nutrient use efficiency and promotion of plant growth, stress tolerance and bioremediation of organic pollutants, pesticides and heavy metals in arable soils, which are beneficial multipurpose properties for sustainable agriculture. The effectiveness of different agricultural wastes in the production of Trichoderma biofertilizers and the industrial production procedures of Trichoderma biomass are discussed.

Keywords: Biocontrol agent; plant growth promotion; stress tolerance; bioremediation

INTRODUCTION

Intensive agricultural practices and climate change have resulted in a loss of biodiversity, a change in pest and pathogen distributions, and chemical contamination of soil, air, and water resources that negatively impact the agroecosystem as well as human health. As agricultural policies are being modified to reduce the use of synthetic chemicals, there is an increasing importance of plant-beneficial fungus Trichoderma in farm practices due to its increased use as a biological alternative to agrochemicals and intensified research linking it to sustainable agriculture (Woo et al., 2023).

Trichoderma is a genus of filamentous fungi that can feed on other fungi (mycotrophism). It is found in virtually all environments, including agricultural land, forest, mountain, grassland, desert, and fresh and marine waters (Harman et al., 2004). Moreover, they are saprophytes, capable of colonizing and degrading dead organic matter. Trichoderma species thrive in all biotopes and have a broad geographic distribution worldwide. Currently, more than 375 species of Trichoderma have been identified (Kubiak et al., 2023). Trichoderma species can reproduce asexually by producing conidia (anamorph form) or sexually by producing ascospores that develop into fruiting bodies (teleomorph form). Additionally, they produce thick-walled spores, called chlamydospores, which help them survive in harsh environmental conditions (Harman et al., 2004). Trichoderma possesses strong cellulolytic and hemicellulolytic properties that allow it to accelerate the hydrolysis of polysaccharides in the cell wall of plant debris (Kumar et al., 2023). This is one of the main characteristics that favor their key application in mass production or industrial production (Kumar et al., 2023). In addition, Trichoderma species produce lignin-modifying enzymes that partially degrade this compound, which reduces its inhibitory effect on microorganisms (Kubiak et al., 2023).

As the challenges in overcoming problems in the agricultural sector have increased significantly in recent years, sustainable strategies with biological control methods are necessary. The versatile role of Trichoderma in sustainable agriculture makes it an excellent choice (Woo et al., 2023). Research interest has therefore expanded to a comprehensive analysis of the versatile properties of Trichoderma as plant-beneficial fungi for applications and improvements in agricultural production. This research interest should be aligned with the ongoing changes in agricultural policy and management and the growing concern for future sustainability.

The most important prerequisite for the commercialization of Trichoderma as a biocontrol or biofertilizer product is its ability for mass production through the economic output of the most significant number of efficient propagules (microsclerotia, conidia, and chlamydospores) in the shortest time (Fravel, 2005; Das and Kim, 2024). The main limitation for commercialization of the end product is the increased production cost due to expensive substrate or carrier materials (Fravel, 2005). However, there has been a growing interest in utilizing agricultural waste to produce biofertilizers or biocontrol products, which can not only promote sustainable agriculture and bring economic benefits to farmers but also reduce the environmental impacts associated with waste disposal. This review highlights the diverse role of Trichoderma in environmentally sustainable agriculture as well as the effectiveness of various agro-wastes in producing Trichoderma biomass.

Multifaceted role of Trichoderma in eco-sustainable agriculture

Trichoderma species are widely used as a key component in soil amendments, soil integrators, biostimulants, bioprotectants, biofertilizers, biodegraders, and bioremediators (Woo et al., 2023). They are particularly of interest to agriculture as biocontrol agents of phytopathogens, even though their many benefits have received considerable attention (Guzman-Guzman et al., 2023). Trichoderma uses direct competition and antagonism, especially in the rhizosphere, where it alters the composition of other microbes and their interactions with them. It has developed the ability to interact with plants through colonization, either on the roots or as an endophyte, and to provide a variety of diverse benefits to its host (Woo et al., 2023). Trichoderma has attracted a lot of interest in research because of its intricate relationship with plants and microorganisms, including its potential to stimulate plant growth, prime local and systemic defenses against biotic and abiotic stresses, and trigger transcriptional memory that affects future plant responses (Woo et al., 2023). Below we have discussed the diverse role of Trichoderma in biocontrol of plant diseases and pests, enhancement of nutrient use efficiency and plant growth promotion, stress tolerance, bioremediation, and above all its ideal characteristics in eco-sustainable agriculture. Figure 1 depicts the multifaceted role of Trichoderma in ecologically sustainable agriculture.

Biocontrol of plant diseases and pests

Since the 1920s, the widespread soil-dwelling fungi Trichoderma has been known to produce antibiotics and parasitize other fungi, which allows them to function as biocontrol agents against a variety of phytopathogens (Harman et al., 2004). It was later discovered that the induction of disease resistance was their primary method of protecting plants (Harman et al., 2004; Abdullah et al., 2021). Trichoderma uses both indirect and direct methods to control plant pathogens. Direct mechanisms involve mycoparasitism and coiling, while indirect mechanisms involve challenges for nutrients and space, acquired resistance, and antibiosis (Woo et al., 2023). The type of Trichoderma strains, the pathogen that is being repelled, including its host, and the ecological context all affect how effective these mechanisms are in the biocontrol strategy (Woo et al., 2023). A variety of pathogenic microorganisms that affect plants have been documented to be controlled by Trichoderma, including bacteria (Pseudomonas, Xanthomonas and Clavibacter), fungi (Fusarium, Botrytis, Colletotrichum, Erysiphe, Magnaporthe, Sclerotinia, Verticillium, Curvularia, Colletotrichum, Alternaria, Rhizoctonia, Athelia, Armillaria, Ustilago, Puccinia), oomycetes (Pythium and Phytophthora), and at least one virulent virus (green mottle mosaic virus) (Harman et al., 2004; Woo et al., 2023). The biocontrol of different Trichoderma species against plant pathogens is shown in Table 1.

Table 1. Biocontrol of different Trichoderma species against plant pathogens

Plant Disease

Crop

Causal agent

Trichoderma spp.

Reference

Bacterial wilt

Tomato (Solanum lycopersicum)

Ralstonia solanacearum

T. asperellum

Konappa et al., 2018

Fungal wilt

Tomato

Fusarium oxysporum

T. asperellum

El Komy et al., 2015

 

Melon (Cucumis melo)

F. oxysporum
T. harzianum

Bernal-Vicente et al., 2009

Leaf spot

Tomato

Xanthomonas euvesicatoria
T. harzianum

T. strigosum

Fontenelle et al., 2011

 

Cucumber (Cucumis sativus)

Pseudomonas syringae 

T. harzianum

T. strigosum

Fontenelle et al., 2011

 

Sugar beet (Beta

vulgaris)

Cercospora

beticola

T. hermatum

Galletti et al., 2008

Damping off

Cucumber

Pythium sp.

T. harzianum

Paulitz et al., 1990

 

Sugar beet (Beta vulgaris)

Rhizoctonia solani

T. harzianum

Lewis and Papavizas, 1987

 

Cotton (Gossyphtm hirsutum)

Rhizoctonia solani

T. hamatum

Lewis and Papavizas, 1987

 

Cotton

Pythium aphanidermatum

T. virens

Howell, 2002

Root rot

Soybean (Glycine max)

Pythium arrhenomanes

T. viride

John et al., 2010

 

Corn (Zea mays)

Fusarium oxysporum

T. viride

John et al., 2010

 

Bean (Phaseolus

vulgaris)

Rhizoctonia

solani

T. asperellum

Asad et al., 2014

 

Pepper plants (Capsicum annuum)

Rhizoctonia solani

T. harzianum

Ahmed et al., 2003

 

Eggplant (Solanum melongena)

Macrophomina phaseolina

T. harzianum

Ramezani, 2008

Stalk rot

Maize (Zea

mays)

Fusarium

graminearum

T. asperellum

Li et al., 2016

Fruit rot

Chili (Capsicum annuum)

Alternaria tenuis

T. harzianum

Begum et al., 2010

 

Tomato

Rhizoctonia solani

T. viride, T. virens, T. harzianum

Amin and Razdan, 2010

Head blight

Wheat and other small grain cereals (Triticum

aestivum)

Fusarium graminearum,

F. culmorum

T. gamsii

Matarese et al., 2012

Sheath blight

Rice (Oryza sativa)

Rhizoctonia solani

T. harzianum

Naeimi et al., 2010

Blossom blight

Alfalfa (Medicago sativa)

Sclerotinia sclerotiorum

T. atroviride

Li et al., 2005

It is relatively complex to control plant diseases caused by bacteria. The use of biocontrol agents is effective at preventing bacterial pathogens and is safer for the environment than chemical bactericides. It was shown that Trichoderma inhibited the growth and survival of Ralstonia. This Gram-negative bacterium causes disease in tomato plants, due to the secretion of lysosime, viridiofungin, and trichokonin (Yan et al., 2021). Additionally, the application of Trichoderma asperellum suppressed bacterial wilt produced by the soilborne bacterium Ralstonia solanacearum, which in turn reduced the disease incidence while simultaneously improving plant growth and yield (Konappa et al., 2018). This was accomplished by increasing the total phenolic contents in plants and inducing the highest level of defense enzyme activities, including peroxidase (POX), polyphenol oxidase (PPO), and phenylalanine ammonia-lyase (PAL), β-1,3-glucanase (Konappa et al., 2018). Biocontrol of bacterial phytopathogens is also illustrated by the induction of resistance by Trichoderma in tomato plants against Xanthomonas euvesicatoria (the causative agent of bacterial spot) and in cucumber plants against angular leaf spot caused by Pseudomonas syringae pv. Lachrymans (Fontenelle et al., 2011). Through a variety of mechanisms, such as lignification, the synthesis of phytoalexins, pathogenesis-related proteins, and secondary metabolites with antimicrobial properties, Trichoderma can protect plants from bacterial pathogens (Kumar et al., 2023).

In addition to plant diseases caused by bacteria, fungi are also often associated with plant diseases and crop damage, resulting in significant losses in agricultural production. Trichoderma has been found to have the ability to eliminate phytopathogenic fungi through various mechanisms, such as mycoparasitism, antibiosis, competition, production of antibiotics and other antifungal compounds, and induced systemic resistance (Kumar et al., 2023).

The process by which one fungus parasitizes another fungus (the host) is called mycoparasitism, and it is one of the key mechanisms of fungal antagonists (Harman et al., 2004). In addition to the pathogen cell wall penetration and host digestion, four sequential processes such as chemotaxis, identification, attachment, and wrapping have been identified as being involved in mycoparasitism (Kumar et al., 2023). Trichoderma koningii colonized injured or infected onion root tissues as a secondary colonizer, reducing Sclerotium cepivorum infection by eliminating the hyphae, rather than invading healthy tissues (Metcalf and Wilson, 2001). Conversely, Trichoderma virens reduced the inoculum potential of several pathogenic fungal species in soil by not only parasitizing their hyphae but also penetrating and destroying some of their resting structures (Howell, 2006). The enzymatic breakdown of cell walls caused by hydrolytic enzymes (such as chitinase, 1,3-glucanase, and cellulase) produced by Trichoderma leads to the degradation of host tissues containing pathogenic organisms (Kumar et al., 2023). It was shown that treating cotton seedlings with T. virens reduced the pre-emergence of damping-off disease caused by Rhizopus oryzae (Howell, 2002).

Antibiosis is the phenomenon whereby a microbe uses secondary metabolites and low molecular weight compounds and antibiotics to prevent or inhibit another organism. Trichoderma synthesizes secondary metabolites such as pyrone, heterocyclic compounds, terpenoids, polyketides, etc. and produces specific low molecular weight compounds and antibiotics to kill plant pathogens (Kumar et al., 2023). The different species of Trichoderma produce different antibiotics; for example, T. viride produces mucortoxins A and B, mucorin, trichophyton, and mucorin; T. mucorin produces mucorin A and B; T. harzianum produces tricholongins BI and BII; T. koningii produces longibrachins and trichokonins; T. atroviride produces atroviridines A-C and neoatroviridines A-D, while other antibiotics and fungicidal compounds have been isolated from T. harzianum, T. koningii, T. aureoviride, T. virens, T. hamatum, and T. lignorum. The koninginin D produced by Trichoderma inhibits the growth of soil pathogens such as Phytophthora solani, Phytophthora middletonii, Phytophthora cinnamomi, Bipolaris sorokiniana, and Fusarium oxysporum (Dunlop et al., 1989). The viridins obtained from Trichoderma species such as T. viride, T. koningii, and T. virens inhibit the germination of spores of Colletotrichum lini, Botrytis allii, Penicillium expansum, Fusarium caeruleum, Stachybotry satra, and Aspergillus niger (Singh et al., 2005). The harzianic acid produced by T. harzianum has antimicrobial activity against Sclerotinia sclerotiorum, Rhizoctonia solani, and Pythium irregular (Manganiello et al., 2018).

Fungal pathogens can be naturally controlled by competition for nutrients (Kumar et al., 2023). Certain characteristics make Trichoderma more competitive than other microorganisms, including a faster growth rate and the ability to mobilize and utilize nutrients from soil and substrate. The saprophytic ability and inoculum potential of Trichoderma are influenced by four primary characteristics: (i) fast germination of fungal propagules and rapid hyphal growth toward nutrients, (ii) production of enzymes that interact with the carbon constituents of the host plant, (iii) secretion of growth inhibitor compounds (fungistatic and bacteriostatic), and (iv) tolerance of competing microorganisms containing fungistatic compounds (Woo et al., 2023). An important factor in the interaction between Trichoderma and plant pathogens is the competition for macro and micronutrients (Harman et al., 2004). Trichoderma has been shown to compete with plant pathogens for nutrients, primarily iron, nitrogen, and carbon (Kumar et al., 2023). Trichoderma species operate as a competitor that aids in the control of plant diseases by producing iron chelating compounds and siderophores that prevent rhizospheric bacteria from obtaining iron, ultimately resulting in the extinction of the disease (Oszust et al., 2020). Studies have also found that Trichoderma can compete with plant pathogens, including Colletotrichum sp., Botrytis sp., and Phytophthora sp., for both complex and simple carbon substrates (Oszust et al., 2020).

Trichoderma confers local or systemic disease resistance by triggering a host plant's defensive mechanism while preventing pathogens from multiplying and growing (Woo et al., 2023). There are generally two methods to achieve Trichoderma-induced plant disease resistance: one is to control the inducers or stimulants that trigger plant disease resistance responses; the other is to use the cell wall-degrading enzymes produced by Trichoderma to release oligosaccharides to cause plant disease resistance (Kumar et al., 2023). It was found that Trichoderma coated corn seeds significantly increased peroxidase activity and phenylalanine ammonia lyase activity, and they proved to be resistant to Curvularia leaf spot (Saravanakumar et al., 2016). An isolate of T. harzianum was reported to induce resistance in tomato plants to bacterial spot (Xanthomonas campestris pv. vesicatoria), reducing disease incidence by 69.32% after 14 days of inoculation (Saksirirat et al., 2009).

Enhancement of nutrient use efficiency and plant growth promotion

Trichoderma can solubilize insoluble minerals via various mechanisms including redox activity and chelating metabolites and plays an important role in soil nutrient cycling (Kashyap et al., 2017). The role of Trichoderma in solubilizing tricalcium phosphate and other phosphorus has been well studied, with results indicating improved phosphorus availability to plants (Saravanakumar et al., 2013). Enhanced availability of P and Fe has been shown with significant increases in plant biomass after Trichoderma harzianum colonized cucumber roots (Yedidia et al., 2001). When T. harzianum was applied to sugarcane, the availability of N, P, and K increased by 27, 65, and 44%, respectively (Singh et al. 2010). The application of T. harzianum together with other bioagents increased the content of N, P, K, Fe, and Mg in chickpea leaves (Kashyap et al., 2017). In comparison to the recommended doses of NPK, Trichoderma biofertilizer increased tomato growth, leaf greenness, and mineral contents (P, K, Ca, Mg, Cu, Fe, Mn, and Zn) in tomato roots. It also produced a 12.9% higher yield (Khan et al., 2016). Trichoderma seed biopriming can cut the amount of nitrogen needed by 30 to 50% for a variety of crops (Harman 2011). These studies suggest that Trichoderma biofertilizers could reduce the need for chemical fertilizers, making them a recommended approach for sustainable agriculture.

Trichoderma are excellent plant growth-promoting fungi (PGPF) as they can produce plant growth-promoting substances such as indoleacetic acid (IAA), auxin and harzianic acid (Contreras-Cornejo et al., 2014). T. virens and T. atroviride were found to produce plant hormones such as indoleacetic acid (IAA) and auxin, and when Trichoderma spp. were inoculated into an Arabidopsis plant, the root tip grew (Contreras-Cornejo et al., 2014). Yedidia et al. (2001) found that a cucumber plant inoculated with T. harzianum significantly increased root biomass and increased the concentrations of Cu, P, Fe, Zn, Mn and Na in the root. Some of the Trichoderma spp. that play an important role as PGPF are listed in Table 2.

Table 2. Inoculation effects of different Trichoderma spp. on plant growth and development

Trichoderma spp.

Plant

Effects

References

T. virens

Arabidopsis

thaliana

Produce the auxin-related compounds indole-3-acetic acid, indole-3-acetaldehyde, and indole-3-ethanol and enhance plant biomass production and lateral root development

Contreras-Cornejo et al., 2009

T. atroviride

Arabidopsis

thaliana

Produce 6-pentyl-2H-pyran-2-one (6-PP), which promoted plant growth and regulated root architecture, inhibiting primary root growth and inducing lateral root formation.

Garnica-Vergara et al., 2016

T. atroviride

Arabidopsis

thaliana

Produce ethylene and improved tolerance to biotic as well as

abiotic stresses

Mukherjee et al., 2013

T. harzianum

Tomato (Solanum

lycopersicum)

Produce harzianolide and increase germination of tomato seeds and improved the growth of the seedlings and root development

Vinale et al., 2013

Cai et al., 2013

T. harzianum

Pea (Pisum

sativum)

Increase the number of lateral root and root length

Naseby et al., 2000

T. harzianum

Cucumber

(Cucumis sativus)

Increase in cumulative root length, root surface area, and the number of root tips

Yedidia et al., 2001

T. harzianum

Brassica (Brassica rapa) and lettuce (Lactuca sativa)

Produce indole-3-acetic acid (IAA) and enhance P solubilization and nutrient mineralization

Asghar and Kataoka, 2021

T. atroviride

Tomato (Solanum lycopersicum)

Release volatile compounds such as 2-heptanone, 2-pentyl furan (2- PF) and 6-pentyl- 2H-pyran-2-one (6- PP), promoting plant growth and suppressing Fusarium wilt disease in tomato seedlings

Rao et al., 2022

Stress tolerance

Drought is one of the principal abiotic stresses that occurs due to water shortage and is exacerbated by rising evapotranspiration (Abdullah et al., 2021). Drought stress causes a significant reduction in the growth and yield of several important crops. Trichoderma inoculation triggers several distinct drought responses in plants (Shukla et al., 2012). For example, T. harzianum was found to postpone or delay the response of rice to drought. This was due to the promotion of root growth independent of water deficit, as evidenced by a delayed increase in the stress-induced metabolites proline, malondialdehyde (MDA) and hydrogen peroxide, as well as an increased concentration of phenolic compounds (Shukla et al., 2012). Inoculation of T. atroviride into maize plants could reduce the deleterious effects of drought and have a function in mediating resistance to stress by stimulating the antioxidant machinery that helps to overcome the unfavorable conditions caused by the overproduction of ROS (Guler et al., 2018). The T. harzianum-inoculated maize plants were shown to have high levels of starch in their leaves, which may be advantageous during drought situations when carbon deprivation is caused by extended stomatal conductance (Akladious and Abbas, 2012).

Apart from drought, cold stress poses a significant risk to the sustainability of crop yields and can result in significant crop losses (Heidarvand and Maali Amiri, 2010). Low temperatures, such as those brought on by unexpected fall frosts, winter freezing temperatures, and late spring cold episodes, can produce this stress in plants (Heidarvand and Maali Amiri, 2010). Trichoderma can suppress the reduction in plant growth and yield caused by cold stress. For instance, it was found that T. harzianum colonization mitigated the negative consequences of cold stress on the majority of commercial tomato cultivars, which are susceptible to cold (Ghorbanpour et al., 2018). T. harzianum inoculation increased the fresh and dry weights of tomato roots and leaves when compared to plants that were cold-treated. Apart from that, there was a decrease in cold injury markers like lipid peroxidation rate and electrolyte leakage and an improvement in photosynthesis and growth rate, leaf water content, and proline accumulation (Ghorbanpour et al., 2018).

Another factor restricting plant growth is soil salinity stress, which is accompanied by high osmotic potential and specific ion toxicity (Rawat et al., 2011). However, the harshness of the saline conditions was lessened when wheat plants were treated with T. harzianum (Rawat et al., 2011). Seed germination was markedly enhanced in both cucumber and Arabidopsis plants when T. asperelloides was inoculated before salt stress was imposed (Brotman et al., 2013). The supply of carbohydrates required for plant growth can be diminished by increased salt stress since it can slow down the photosynthetic rate (Ahmad et al., 2015). The photosynthetic pigment of the Indian mustard plant grown under saline conditions was significantly restored after being inoculated with T. harzianum (Ahmad et al., 2015). With T. asperellum inoculation, genes related to ROS metabolism and plant defense response were found to be up-regulated (Doni et al., 2019). Table 3 lists the alleviation of abiotic stress responses of plants after inoculation with Trichoderma spp.

Table 3. The alleviation of abiotic stress responses of plants following inoculation with Trichoderma spp.

Abiotic stress

Trichoderma spp.

Plants

Stress alleviation mechanism

References

Drought

T. harzianum

Rice (Oryza sativa)

Postpone or delay the response of rice to drought by delaying the release of stress-induced metabolites proline, malondialdehyde (MDA), and hydrogen peroxide, as well as by increasing the concentration of phenolic compounds

Shukla et al., 2012

T. atroviride

Maize

Stimulated the antioxidant machinery that helps to overcome drought stress by the overproduction of ROS

Guler et al., 2018

T. harzianum

Maize

Produced high levels of starch in leaves, which may be advantageous during droughts when extended stomatal conductance cause carbon deprivation

Akladious and Abbas, 2012

T. harzianum

Tomato

Increased secondary metabolites and proline content

Mona et al., 2017

Cold

T. harzianum

Tomato

Decreased cold injury markers, such as lipid peroxidation and electrolyte leakage, and an improvement in photosynthesis and growth rate, leaf water content, and proline accumulation

Ghorbanpour et al., 2018

Salinity

T. asperelloides

Arabidopsis,

Cucumber

Improved seed germination

Brotman et al., 2013

T. harzianum

Indian mustard

Restored photosynthetic pigment level

Ahmad et al., 2015

T. asperellum

Rice

Up-regulation of genes related to ROS metabolism

Doni et al., 2019

Bioremediation

Bioremediation with Trichoderma in agriculture is an excellent natural method to maintain soil fertility and increase crop yields (Zin and Badaluddin, 2020). The ability of Trichoderma to metabolize various pesticides has been demonstrated. Herbicides containing sulfonylurea are commonly used in agriculture to suppress weed growth (Vazquez et al. 2015). However, sulfonylurea kills beneficial soil microorganisms due to its non-targeted effects. Fortunately, Trichoderma has the ability to degrade sulfonylurea herbicides (Zin and Badaluddin, 2020). For example, Vazquez et al. (2015) found that T. harzianum can detoxify metsulfuron-methyl, a sulfonylurea herbicide. Trichoderma uses sulfosulphuron as a carbon source and detoxifies it by breaking down the sulfonylamide bond and the sulfonylurea bridge (Yadav and Choudhury, 2014).

Insecticides such as dichlorvos (DDVP) are frequently used in agriculture, with excessive residues in the soil endangering ecosystems and human health (Sun et al., 2019). A protein encoding a TaPon1-like protein is present in T. atroviride strain T23 and contributes to the effective biodegradation activity of DDVP (Sun et al., 2019). Carbendazim is a systemic fungicide commonly used to control soilborne diseases caused by a variety of phytopathogenic fungi (Sharma et al. 2016). However, it has been discovered to be a significant pollutant in agricultural land. Sharma et al. (2016) reported that T. harzianum, T. viride and T. amurensis could effectively degrade carbendazim within 5 days of application. Another fungicide, penthiopyrad, which is used to control foliar and soil fungal diseases in fruit, nut and vegetable crops, was also effectively degraded by T. harzianum (Linhart et al., 2019).

Commonly used pesticides are synthetic polycyclic aromatic hydrocarbons (PAHs) such as benzo[a]pyrene, pyrene and phenanthrene. However, PAHs are among the most critical environmental pollutants due to their toxic, immobile and bioaccumulative properties (Zin and Badaluddin, 2020). In PAH-contaminated soil, T. asperellum H15 has been shown to efficiently degrade benzo[a]pyrene, pyrene, and phenanthrene by up to 81%, 63%, and 74%, respectively (Zafra et al., 2015). There is evidence that catechol 1,2 dioxygenase, laccase, and peroxidase enzymes play a key role in the degradation of PAHs by T. asperellum (Zafra et al. 2015).

Studies have shown that T. harzianum can effectively degrade a variety of harmful organic pollutants, including phenols, cyanides and nitrates (Huang et al., 2018). Trichoderma species have been shown to degrade several artificial dyes, including pentachlorophenol, endosulfan, and dichlorodiphenyl trichloroethane (DDT) (Katayama and Matsumura, 1991). In the bioremediation of Cr (VI)-contaminated wastewaters, T. inhamatum consistently reduced Cr (VI) levels to a significant extent (Morales-Barrera and Cristiani-Urbina, 2008). Similarly, T. harzianum has been reported to be effective in remediating cadmium-contaminated soils (Faedda et al., 2012). The different species of Trichoderma as bioremediators for various pollutants are presented in Table 4.

Table 4. Bioremediation of pollutants by different species of Trichoderma

Pollutants

Trichoderma spp.

Effects

References

Metsulfuron methyl (Herbicide)

T. harzianum

Detoxification of the herbicide up to 100%

Vázquez et al., 2015

Dichlorvos (Insecticide)

T. atroviride

Efficient degradation of the insecticide

Sun et al., 2019

Carbendazim (Fungicide)

T. harzianum

85% of degradation within 5 days

Sharma et al., 2016

 

T. atroviride

50% of degradation within 5 days

 

 

T. viride,

20% of degradation within 5 days

 

Penthiopyrad (Fungicide)

T. harzianum

60% of degradation within 14 days

Linhart et al., 2019

Benzo[a]pyrene

T. reesei

54% degradation after 12 days of incubation

Yao et al. (2015)

Benzo[a]pyrene

T. asperellum

81%, degradation in soils

Zafra et al., 2015

Pyrene

T. asperellum

63%, degradation in soils

Zafra et al., 2015

Phenanthrene

T. asperellum

74%, degradation in soils

Zafra et al., 2015

Carbendazim and Mancozeb

Trichoderma spp.

25% degradation of Carbendazim and 36% degradation of Mancozeb during 15 days of incubation

Ahlawat et al., 2010

Lead (Pb), Chromium

(Cr)

T. viride

Uptake of 9.14 mg/g of lead and 2.55 mg/g of Chromium

Kumar et al., 2023

Copper (Cu)

T. atroviride

50-85% of Cu adsorption during in vitro experiment

Yazdani et al., 2009

Zinc (Zn)

T. atroviride

47.6 – 64% adsorption and 30.4 – 45% absorption of Zn

Yazdani et al., 2010

Cadmium (Cd)

T. asperellum

76.17% removal of Cadmium

Mohsenzadeh and

Shahrokhi, 2014

Production of Trichoderma biofertilizer from agro-waste

There are multiple stages involved in industrial production of Trichoderma, including harvesting, drying, formulation, and storage. These steps can have a significant impact on the number of microorganisms and their viability, and consequently on the shelf life and bioefficacy of the end product (Kumar et al., 2023). The nutrient-rich, low-cost, and readily available organic substrates are needed to sustain a robust fungal growth. Agro-industrial waste possesses these properties and can be used for the large-scale production of the fungal biomass.

Several reports describe the production of Trichoderma biomass containing synthetic media such as cellulose, glucose, molasses, and starch (Kumar et al., 2023). However, the high cost of these raw materials for the commercially viable production of biocontrol agents is one of the main reasons for their limited application. For the mass production of Trichoderma, numerous studies have used low-cost substrates such as composted coir and coffee waste (Saratale et al., 2020; Van Gerrewey  et al., 2020), poultry manure and coffee waste (Sawant and Sawant, 1996), neem cake, degraded coffee pulp, cow dung, and coir pith (Saju et al., 2002), sorghum grain floor, sawdust, wheat bran, groundnut shell, molasses, farm-produced waste, biogas plant extract, dried cow dung, neem cake, talc, mushroom compost, fly ash, peat soil (Sangle and Bambawale, 2005), fruit, vegetables, and crop wastes, poultry manure and farm-yard manure (FYM) (Simon, 2011), rotten wheat grains, sugarcane bagasse, fruit juice waste, and vegetable and fruit wastes (Babu and Pallavi, 2013). For large-scale production of Trichoderma, a variety of easily accessible and reasonably priced local organic media, including neem cake, coconut husk, and decomposed coffee pulp, have been suggested (Saju et al., 2002). Organic fertilizers like vermiculite, neem cake, and mushroom composts were found to be effective carriers for mass production of Trichoderma (Mustafa et al., 2009). Neem cake enriched with Trichoderma talcum powder is suggested for the treatment of coconut basal stem rot and areca nut and coconut stem bleeding (Mustafa et al., 2009). Due to the scarcity of premium neem cakes and their high cost in commercial formulations, farmers are now in need of viable biological control agents with affordable formulations for disease prevention (Kumar et al., 2023). In recent years various agro-wastes have been successfully tested for pilot-scale production of Trichoderma (Table 5).

Table 5. Different agro-waste carrier materials and their efficacy in Trichoderma biomass production

Agro-waste carrier materials

Composition/Components

Efficacy

References

Cow dung

 

Decomposed cow dung + Trichoderma formulation

37.5  × 107 cfu/g

Mohiddin et al., 2017

Coffee husk + Cow dung

 

Coffee fruit skin decomposed with cow dung + poultry manure + T. harzianum suspension

9 × 1011 to 3 × 1012

cfu/g substrate

Sawant and Sawant, 1996

Banana waste

Banana waste (chopped 5–6 cm length) + rock phosphate+ T. harzianum supension

 

Thangavelu et al., 2004

Wheat seeds

 

Grinded grain + sugar solution (1%) + T. harzianum

38 × 107 cfu/g

Mohiddin et al., 2017

Vermiculite + Oat +

bentonite

 

Oat (20 g) + bentonite (50 mL) + vermiculite + T.

harzianum + water (60 mL)

Maintained cfu after

8 weeks

Martínez-Medina et al., 2009

Rice straw

Fifty grams of soil + rice straw (5 g) + Trichoderma

biomass (500 mg)

5.3 × 1010 cfu/g

Organo et al., 2022

Rice powder

 

Sterilized rice powder + dextrose + talc powder +

T. viride

cfu/g 10 × 109 up to

six months at room

temperature

Rini et al., 2018

Molasses

Molasses yeast extract (MYE) medium+ glycerol (3%) (V/V) +T. harzianum + Talc powder

Extended the

shelf-life for 7 to

12 months

Sriram et al., 2011

Isolation and identification of specific Trichoderma species are essential steps that should be performed before biomass production. After isolation and characterization of a pure culture of Trichoderma, hyphae, chlamydospores or conidia can be used as propagation material (propagules). Both solid-state fermentation and submerged (liquid) fermentation can be used for the mass production of Trichoderma. Since solid-state fermentation can promote the formation of more spores, using agricultural waste to produce inoculants would be a better choice for solid-state fermentation (Kumar et al., 2023). The following processes can be used for the industrial production of Trichoderma: (1) optimization of culture conditions in the laboratory to achieve high yield and biomass; (2) optimization of biomass production at the pilot plant level to identify and solve different technical variables; (3) integration of specific unit operations from fermentation, bioseparation and formulation into a single process; and (4) production of Trichoderma on an industrial plant scale. The final product can then be tested for suitability for field applications (Abdullah et al., 2021). To improve the shelf-life and effectiveness of Trichoderma formulations, attempts have been made to create efficient and successful techniques, such as microencapsulation using various polymers, adjuvants, or carriers (Kumar et al., 2023).

Utilizing agricultural waste for biofertilizer production has its challenges, including contamination from heavy metals, pesticides, pathogens, and salts, as well as nutrient imbalances (Bhatia and Sindhu, 2024). There is also a risk of plant damage, such as smothering or scorching, an increased likelihood of disease transmission, and environmental pollution due to improper disposal methods like burning or leaching (Lackner and Besharati, 2025). To address these issues and safeguard soil and crop health, thorough evaluation and pre-treatment are essential. Certain agricultural waste can introduce toxic heavy metals, including lead, arsenic, and mercury, along with harmful chemicals into the soil, which can endanger humans, animals, and plants (Bhatia and Sindhu, 2024). Additionally, waste may carry pesticide residues that negatively affect beneficial soil microorganisms and can infiltrate the food chain. Animal manure and similar waste can contain bacteria, viruses, and parasites that pose health risks to livestock, humans, and other environmental elements (Bhatia and Sindhu, 2024). Although beneficial, the excessive use of certain waste materials, such as manure, can result in nutrient imbalances, leading to high potassium or magnesium levels that may adversely affect livestock grazing on treated pastures, potentially causing conditions like hypomagnesaemia (Lackner and Besharati, 2025). Some waste materials decompose at a slow rate, which can initially bind nutrients and impede plant growth (Lackner and Besharati, 2025). The management of biofertilizer derived from agricultural waste requires careful consideration of the following factors: (1) Pre-treatment: Waste materials typically need treatment, such as composting or biosorption, to eliminate contaminants and prepare them for fertilization, (2) Proper Application: It is vital to manage application rates and methods meticulously to prevent nutrient imbalances, plant damage, and disease spread, and (3) Source Assessment: Understanding the origin of the waste and evaluating it for potential contaminants is crucial before its use as a carrier material for biofertilizer production.

CONCLUSIONS

Trichoderma provides the following attributes for sustainable agriculture: (1) direct biocontrol of plant pests and diseases, which removes the need for chemical pesticides; (2) broad-ranging biocontrol activities against insects, nematodes, and pathogenic microorganisms; (3) activation of plant defense mechanisms, which provides indirect biocontrol of plant pests and diseases; (4) activation of plant defense mechanisms, which increases tolerance to abiotic stress; (5) stimulation of plant growth, which increases crop yields and productivity; (6) improvement of soil nutrient availability, which increases plant uptake and assimilation; and (7) stimulation of bioremediation of pesticides, organic pollutants, and heavy metals in arable soils. To optimize the benefits of this green fungus and promote safer, environmentally sustainable agriculture, multidisciplinary research is required to comprehend its multifunctional characteristics. Efforts to elucidate the molecular basis of plant growth promotion and defense activation by Trichoderma are needed to gain a broad perspective on their functions and suitability for climate-resilient agriculture. More research is needed to find more affordable alternative substrates (e.g., agricultural waste) and optimal operating conditions to increase the yield of Trichoderma biomass.

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