Conservation of Agricultural Soil Using Entomopathogenic Fungi: An Agent With Insecticides Degradation Potential

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Abstract

A major current focus in agricultural soil conservation is to ensure a pest control program is sustainable, and therefore, entomopathogenic fungi have been considered and extensively studied as biopesticides. However, the ecological role of entomopathogenic fungi in degrading insecticides in soil is not well understood. In this study, the potential of entomopathogenic fungi Metarhizium anisopliae (Met.) in degrading two common agricultural insecticides, chlorpyrifos and cypermethrin was investigated by introducing M. anisopliae into autoclaved soils artificially contaminated with 500 ppm of chlorpyrifos, and cypermethrin. The concentration of chlorpyrifos and cypermethrin were determined after 21 days using UPLC/PDA detector. The residues, rate, and percentage of degradation between insecticides treated and control soil were compared using an independent t-test (SPSS 20.0). The degradation of both insecticides in Met. treated soil (>80%) was significantly higher than control soil (47-61%). The residues for chlorpyrifos and cypermethrin residue in Met. treated soils were 19.39±0.10 ppm and 19.68±0.36 ppm, respectively, significantly lower than control (residues of chlorpyrifos-262.6±7.6 ppm and cypermethrin-194.4±4.3 ppm, at p<0.05). The results suggested M. anisopliae may play a role in the bioremediation of soil.

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Microbial degradation of organophosphorus compounds.

J. B. Singh, A. Walker (2006)

Synthetic organophosphorus compounds are used as pesticides, plasticizers, air fuel ingredients and chemical warfare agents. Organophosphorus compounds are the most widely used insecticides, accounting for an estimated 34% of world-wide insecticide sales. Contamination of soil from pesticides as a result of their bulk handling at the farmyard or following application in the field or accidental release may lead occasionally to contamination of surface and ground water. Several reports suggest that a wide range of water and terrestrial ecosystems may be contaminated with organophosphorus compounds. These compounds possess high mammalian toxicity and it is therefore essential to remove them from the environments. In addition, about 200,000 metric tons of nerve (chemical warfare) agents have to be destroyed world-wide under Chemical Weapons Convention (1993). Bioremediation can offer an efficient and cheap option for decontamination of polluted ecosystems and destruction of nerve agents. The first micro-organism that could degrade organophosphorus compounds was isolated in 1973 and identified as Flavobacterium sp. Since then several bacterial and a few fungal species have been isolated which can degrade a wide range of organophosphorus compounds in liquid cultures and soil systems. The biochemistry of organophosphorus compound degradation by most of the bacteria seems to be identical, in which a structurally similar enzyme called organophosphate hydrolase or phosphotriesterase catalyzes the first step of the degradation. organophosphate hydrolase encoding gene opd (organophosphate degrading) gene has been isolated from geographically different regions and taxonomically different species. This gene has been sequenced, cloned in different organisms, and altered for better activity and stability. Recently, genes with similar function but different sequences have also been isolated and characterized. Engineered microorganisms have been tested for their ability to degrade different organophosphorus pollutants, including nerve agents. In this article, we review and propose pathways for degradation of some organophosphorus compounds by microorganisms. Isolation, characterization, utilization and manipulation of the major detoxifying enzymes and the molecular basis of degradation are discussed. The major achievements and technological advancements towards bioremediation of organophosphorus compounds, limitations of available technologies and future challenge are also discussed.

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Pest toxicology: the primary mechanisms of pesticide action.

John E. Casida (2009)

Pesticides are used to control pests before they harm us or our crops. They are selective toxicants in the form and manner used. Pesticides must be effective without human or crop injury. They must also be safe relative to human and environmental toxicology. The study of how the pesticide works on the pest is referred to here as pest toxicology. About 700 pesticides, including insecticides, herbicides, and fungicides, act on perhaps 95 biochemical targets in pest insects, weeds, and destructive fungi. Current insecticides act primarily on four nerve targets, i.e., acetylcholinesterase, the voltage-gated chloride channel, the acetylcholine receptor, and the gamma-aminobutyric acid receptor, systems which are present in animals but not plants. Herbicides act mostly on plant specific pathways by blocking photosynthesis, carotenoid synthesis, or aromatic and branched chain amino acid synthesis essential in plants but not mammals. Many fungicides block ergosterol (the fungal sterol) or tubulin biosynthesis or cytochrome c reductase, while others disrupt basic cellular functions. A major limiting factor in the continuing use of almost all pesticides is the selection of strains not only resistant to the selecting or pressuring compounds but also cross-resistant to other pesticides acting at the same target. One approach to reinstating control is to shift from compounds with the resistant target site or mode of action to another set which have a sensitive target. This type of pesticide management led to the formation of Resistance Action Committees for insecticides, herbicides, and fungicides with very knowledgable experts to define resistance groups, which are in fact listings of primary target sites in pest toxicology. Continued success in pest and pesticide management requires an understanding of comparative biochemistry and molecular toxicology considering pests, people, and crops. Defining and applying the principles of pest toxicology are critical to food production and human health.

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Biodegradation of Chlorpyrifos and Its Hydrolysis Product 3,5,6-Trichloro-2-Pyridinol by a New Fungal Strain Cladosporium cladosporioides Hu-01

Shaohua Chen, Chenglan Liu, Chuyan Peng … (2012)

Intensive use of chlorpyrifos has resulted in its ubiquitous presence as a contaminant in surface streams and soils. It is thus critically essential to develop bioremediation methods to degrade and eliminate this pollutant from environments. We present here that a new fungal strain Hu-01 with high chlorpyrifos-degradation activity was isolated and identified as Cladosporium cladosporioides based on the morphology and 5.8S rDNA gene analysis. Strain Hu-01 utilized 50 mg·L−1 of chlorpyrifos as the sole carbon of source, and tolerated high concentration of chlorpyrifos up to 500 mg·L−1. The optimum degradation conditions were determined to be 26.8°C and pH 6.5 based on the response surface methodology (RSM). Under these conditions, strain Hu-01 completely metabolized the supplemented chlorpyrifos (50 mg·L−1) within 5 d. During the biodegradation process, transient accumulation of 3,5,6-trichloro-2-pyridinol (TCP) was observed. However, this intermediate product did not accumulate in the medium and disappeared quickly. No persistent accumulative metabolite was detected by gas chromatopraphy-mass spectrometry (GC-MS) analysis at the end of experiment. Furthermore, degradation kinetics of chlorpyrifos and TCP followed the first-order model. Compared to the non-inoculated controls, the half-lives (t 1/2) of chlorpyrifos and TCP significantly reduced by 688.0 and 986.9 h with the inoculum, respectively. The isolate harbors the metabolic pathway for the complete detoxification of chlorpyrifos and its hydrolysis product TCP, thus suggesting the fungus may be a promising candidate for bioremediation of chlorpyrifos-contaminated water, soil or crop.