ArticleLiterature Review

Toxic effects of organophosphate pesticide monocrotophos in aquatic organisms: A review of challenges, regulations and future perspectives

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Abstract

In recent times, usage of pesticide, herbicides and synthetic fertilizers in farming lands has made the environment worse. The pesticide residues and toxic byproducts from agricultural lands were found to contaminate the aquatic ecosystem. The misuse of synthetic pesticide not only affects the environment, but also affects the health status of aquatic organisms. The organophosphate pesticide pollutants are emerging contaminants, which threatens the terrestrial and aquatic ecosystem. Monocrotophos (MCP) is an organophosphate insecticide, utilized on crops including rice, maize, sugarcane, cotton, soybeans, groundnuts and vegetables. MCP is hydrophilic in nature and their solubilizing properties reduce the soil sorption which leads to groundwater contamination. The half-life period of MCP is 17–96 and the half-life period of technical grade MCP is 2500 days if held stable at 38 °C in a container. MCP causes mild to severe confusion, anxiety, hyper-salivation, convulsion and respiratory distress in mammals as well as aquatic animals. The MCP induced toxicity including survival rate, behavioural changes, reproductive toxicity and genotoxicity in different aquatic species have been discussed in this review. Furthermore, the ultimate aim of this review is to highlight the international regulations, future perspectives and challenges involved in using the MCP.

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... Field application dose of monocrotophos is 0.25-1.5 kg/ ha and the half-life is approximately 17-96 days in environment (Kaur and Goyal., 2019). It is reported that monocrotophos showed its half-life around 2500 days in 38º C in closed environment (Rajan et al., 2023). Several studies have revealed toxic potential of monocrotophos in non-target organisms. ...
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Current study investigated the chronic effect of monocrotophos exposure, a globally used pesticide on 3rd instar larvae and pupae of fruit fly Drosophila melanogaster. Study commenced with the investigation of chronic median lethal concentration (LC50) which was found as 0.68 µg/mL for 3rd instar larvae and 0.56 µg/mL for pupae. Accordingly five sub-lethal concentrations such as 0.2, 0.25, 0.3, 0.35 and 0.4 µg/mL were selected for experimental set up. Treated larvae manifested altered feeding habit, changed life cycle duration and reduced body weight and length in both larval and pupal stage. Interestingly alteration in sex-ratio and gender biased population was encountered after exposure to monocrotophos. Since D. melanogaster shares significant molecular and physiological homologies with higher vertebrates, hence the present findings could be alarming for other non-targeted organisms who are getting direct or indirect chronic exposure to this chemical.
... The imbalance between the production and elimination of free radicals induced by BF exposure may be responsible for this disorder (Fatima et al., 2007;Karthick et al., 2024;Wang et al., 2021b). The excess ROS inhibits the activity of SOD, CAT and GSH (Lushchak, 2011;Zhang et al., 2020a), leading to a decrease in their levels in CGS larvae. ...
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... us, increasing the susceptibility of cells to reactive oxidative intermediate attacks and alters membrane integrity, fatty acid compositions, antioxidant status, and cellular dysregulation. [15,16,19,[21][22][23][24][25][26][27] Under physiological conditions, ROS are cleared from the cells by the actions antioxidant enzymessuperoxide dismutase (SOD), catalase (CAT), thiols, or GSH. [28][29][30] Fortunately, under normal physiological conditions, the balance between free radical generation in tissues and endogenous antioxidants enzymes' activities prevents oxidative stress from building up. ...
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Pesticides are an integral part in maintaining agriculture and horticultural productivity and play a vital role in meeting the increasing food, fiber, and fuel needs of the growing population. Globally, organophosphate pesticides (OPPs) are among the most common pesticides used due to their high proficiency and relatively low persistence in the environment. However, recent studies have reported problems due to pesticide use, e.g., phorate contamination of aquatic ecosystems (fresh and groundwater), sediments, fruits and vegetables, and forage crops. This review highlights many cases where phorate has been detected above its respective maximum residue limit values. Organophosphate pesticides, including phorate, have negative impacts on both the environment and human health. The ecological and public health concerns of recurrent pesticide utilization have encouraged the research related to environmental fate of pesticides. Bioremediation is an effective, eco-friendly, and financially viable approach for the decontamination and degradation of toxic OPPs from the environment, compared to the costly, unecological, and time-consuming physicochemical approaches, which lead to the generation of byproducts of higher toxicity. Researchers have recognized that a wide range of microbes, mainly bacteria, can degrade this extremely hazardous pesticide. Therefore, this review discusses the present pesticide scenarios, especially phorate contamination, its toxicity, biodegradation, and metabolic products via bacterial communities, both in India and globally. The latest and up-to-date literatures on the use, contamination, and bacterial application of phorate degradation are also summarized. This article offers national and international food safety organizations and public health authorities the ability to be involved in preventing the risks associated with the use of food and nutrition products contaminated with extremely toxic phorate pesticide. This article would also enable researchers to develop comprehensive and sustainable methods to effectively remediate pesticide-contaminated environments. In conclusion, it is envisaged that the successful application of bacterial communities for degradation of phorate would help in understanding the fate and persistence of such toxic pollutants in a better way.
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Fish bioconcentration factors (BCF) are used for the prediction of the environmental effects of new chemicals and some studies have suggested that they can be predicted from the Physico-chemical properties of the chemical. The rigorous use of pesticides resulted in the dispersal and persistence of pollutants throughout the ecosystem. Pesticides contamination in the aquatic ecosystem has become one of the most staggering issues due to their detrimental effect on public health and the environment. This study aimed to investigate the bioconcentration factor of pesticides monocrotophos and quinalphos in three tissues (skin, muscles, gills) of the fish Channa striatus for 21 days, of the three analyzed tissues of monocrotophos exposed fish, gill accumulated highest concentration of (0.033 mg kg-1) while muscles (0.012 mg kg-1) at the lowest, whereas the concentration of quinalphos was maximum (0.98mg kg-1) in liver and minimum (0.074 mg kg-1) in muscle. Results showed that the effect of pesticide differs from tissue to tissue. However, the levels exceeded maximum detection limits as recommended by U.S. Geological Survey National Water Quality Laboratory, Denver, Colo. Hence it is suggested that the fish containing pesticide residues beyond permissible limit should be avoided for food purposes.
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Organophosphate poisoning is a continued menace associated with high morbidity and mortality in both resource-crunched developing and developed countries. Cases have been described of deliberate self-poisoning which has higher mortality than accidental exposure. Fatal poisoning by accidental dermal absorption is rarely reported for monocrotophos. Authors detail fatal accidental monocrotophos poisoning in adult female by dermal exposure while sleeping. Pesticide was detected in post-mortem blood and skin by chromatography and spectroscopy. Extraction along with review of literature for monocrotophos poisoning is adjuncted in this study.
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Monocrotophos, commonly named Azodrin or Nuvacron, is an organophosphate insecticide, which in spite of ban is preferred due to its high efficacy against insect pests. With a field application dose of 0.25–1.5 kg ha⁻¹, it has median lethal dose (LD50) of 18–20 mg kg⁻¹ for mammals and half-life of 17–96 days. Monocrotophos uncontrolled application in farming has led to the contamination of surface and groundwater, causing neurotoxicity, genotoxicity, hyperglycaemic and stressogenic effects on different organisms. Being readily soluble in water, it is grouped under class I: highly toxic compounds. Microbes such as Bacillus, Pseudomonas, Aspergillus, Anabaena and Nostoc at 25–37 °C and pH 5.5–8.5 have the ability to utilize monocrotophos as nutrient source and can tolerate up to 500–1200 mg L⁻¹ of monocrotophos, causing its complete or partial degradation to dimethyl phosphate, phosphoric acid, valeric or acetic acid. On the other hand, generation of ·OH radicals by photoactivation of the catalyst such as TiO2 and ZnO leads to complete mineralization of monocrotophos. Biodegradation followed by photocatalytic degradation would be the most efficient and sustainable approach. This review focuses on toxicity, fate of monocrotophos in the environment and its microbial and photocatalytic degradation.
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Several studies have demonstrated that high glucose feeding induced oxidative stress and apoptosis thereby affecting growth, fertility, aging and lifespan in Caenorhabditis elegans. Earlier studies from our laboratory have clearly established the propensity of monocrotophos, an OPI to alter the physiological and behavioural responses of C. elegans. The present study was aimed to investigate the effect of monocrotophos (MCP) on physiological / behavioural and biochemical responses in C. elegans that were maintained on high glucose diet. We exposed the worms through development to high glucose diet (2%) and then treated with sublethal concentrations of MCP (0.5, 0.75, 1.5 mM). We measured the behavioural responses in terms of locomotion, physiological responses in terms of egg laying, brood size, lifespan; morphological alterations; and biochemical responses including glucose content. The worms exposed from egg stage through development to high glucose diet showed enhanced toxic outcome of MCP in terms of physiological, behavioural and biochemical responses. Our studies showed that C. elegans is a good model to study glucose-OPI interactive neurotoxicity since all the responses could be studied at ease in this organism and the outcome could be well extrapolated to those that one would expect in higher animals.
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Objective: Pesticides are stable compounds and they enter the aquatic ecosystem through the agriculture run off. The evaluation of nature and degree of harmful effects produced by the toxic substance in the aquatic organisms are evaluated by toxic tests. The 96 hour LC50 values have generally been found to be satisfactory for the measurement of acute toxicity. The differences in 96 h LC50 of the same toxicant in different fishes may be attributed to individual traits including those of behavior and additional structure such as accessory respiratory organs. The individual characters such as size and weight, sex and biological behavior are important determination for variation in LC50 Methods: Therefore, in this present study is an attempt to study the toxicity of the pesticide with respect to the hematology, biochemical and histology of fish Labeo rohita (Ham). The Monocrotophos affects not only fish but also organisms in the food chain through the process of consumption of one by the other. The pesticide, which enters the body tissues of the fish, affects the physiological activities. values. Results: The cytometric measurements of erythrocytes of sublethal exposure showed that there is not much differences from the control. In the control fish, the erythrocytes were oval in shape with elongated nucleus. Fish, exposed to sublethal concentration of Monocrotophos showed abnormal size Reduction in the volume of the cytoplasm of cells and swelling of nuclei were observed in fish exposed to concentration. In the hematology, the total Red Blood Corpuscle and Haemoglobin content were decreased with the increasing hours of exposure of the monocrotophos 36% EC. The amount of the Mean Corpuscular Haemoglobin (MCH) also was increased. The haemoglobin content directly relationship for RBC content it indicate count leading to anemia as a result of inhibition of erthropoiesis, haemosynthesis and increase in the rate of erythrocyte destruction in haemopoietic organs. However, the total was total White Blood Corpuscle was increased with the increasing hours of exposure of the Monocrotophos 36% E. C. The constant increasing in the differential count clearly indicates that the pesticide stress certainly stimulate the white blood cells to produce more at all time of exposure. A linear relationship was established with respect to pesticide monocrotophos and total White Blood Corpuscle. The constant increase in the differential count clearly indicates that the pesticide stress certainly stimulate the white blood cells to produce more at all times of exposure. Conclusion: It has been suggested that the enumeration of differential cell ratio counts provide of useful diagnostic procedure to assess the physiological stress in the fish.
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Cross-regulation occurs at many points between the hypothalamic-pituitary-gonad (HPG) and hypothalamic-pituitary-thyroid (HPT) axes. Monocrotophos (MCP) pesticide could disrupt HPG and HPT axes, but its direct target within the endocrine system is still unclear. In the present study, hormone concentrations and transcriptional profiles of HPG and HPT genes were examined in male goldfish (Carassius auratus) exposed to 0, 4, 40, and 400 μg/L MCP for 2, 4, 8, and 12 d. In vivo data were analyzed by multiple linear regression and correlation analysis, quantitatively indicating that MCP-induced plasma 17β-estradiol (E2) levels were most associated with alteration of cyp19a transcription, which was also a potential point indirectly modulated by the MCP-altered thyroid hormones (THs) status; disturbance of THs pathways was most related with effect of MCP on regulation of the hypothalamic-pituitary hormones involved in the thyroid system, and the increased E2 levels might enhance the impact of MCP on HPT axis by modulating hepatic deiodinase expression. Our finding, based on these correlational data, gave a whole view of the regulations, especially on the cross-talk between sex hormone and thyroid hormone pathways upon exposure to chemicals with unknown direct target in vivo, and cautions should be exercised when developing adverse outcome pathway networks for reproductive and thyroidal endocrine disruption.
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One of the major classes of pesticides is that of the organophosphates (OPs). Initial developments date back almost two centuries but it was only in the mid-1940s that OPs reached a prominent status as insecticides, a status that, albeit declining, is still ongoing. OPs are highly toxic to non-target species including humans, the primary effects being an acute cholinergic toxicity (responsible for thousands of poisoning each year) and a delayed polyneuropathy. Several issues of current debate and investigation on the toxicology of OPs are discussed in this brief review. These include 1) possible additional targets of OPs, 2) OPs as developmental neurotoxicants, 3) OPs and neurodegenerative diseases, 4) OPs and the "aerotoxic syndrome", 5) OPs and the microbiome, and 6) OPs and cancer. Some of these issues have been debated and studied for some time, while others are newer, suggesting that the study of the toxicology of OPs will remain an important scientific and public health issue for years to come.