High levels of Co(NO3)2 for living organisms are toxic. In this study, the protective effects of 2,6-dimethyl-morpholine dithiocarbamate (DMMDTC) against the toxicity of Co(NO3)2 on Allium cepa L. were investigated. Seven groups of onion bulbs were established to investigate the potential effects of DMMDTC against Co(NO3)2 exposure in root tips. These are a control group, two groups of DMMDTC alone in different concentrations, two groups of Co(NO3)2 in different concentrations, and finally, two groups of combined DMMDTC (1,2) + Co (1,2) in different concentrations were applied to onion roots. The effects of the chemicals on physiological parameters, Mitotic Index (MI), Micro Nucleus (MN), genotoxicity and Co(NO3)2 accumulation in the roots were examined. MI analysis revealed that Co(NO3)2 treatments reduced the MI compared to water control by 52.2-46.6%, depending on the concentration. The combinations of DMMDTC + Co(NO3)2 significantly increased MI while decreasing MN compared to the cobalt-only treatments. However the protective effect of DMMDTC against cobalt toxicity was limited when the data compared to the water control. The heavy damage to epidermis cells and nucleus was also observed in those cobalt applied groups. Co(NO3)2 accumulation in the roots, compared to water control, was also high in Co1-Co2 groups. The DMMDTC used in this study had effects similar to those of plant extracts in reducing genotoxic effects. Therefore, the research highlights the potential benefits of using synthesized DMMDTC on Allium cepa against the toxic effects of cobalt.

Profenofos is one of the most widely used toxic organophosphate insecticides used in crop fields against various insect pests. The pesticide may spread into the environment through various sources, such as air, water, soil, etc. Therefore, there is a high risk of ingestion for animals and aquatic fauna. The present study aimed to assess the profenofos-induced hepatotoxicity, genotoxicity, and haematological abnormalities of the freshwater fish Channa punctatus, which can indicate the probable threat of this pesticide to other species, including humans. Freshwater fish Channa punctatus were exposed to two sub-lethal concentrations of Profenofos (0.078 and 0.157 mg/L). After 7 days of consecutive exposure, changes in haematological parameters, hepatic tissue histology, and genotoxic effects were evaluated. The total count of red blood cells (RBCs), white blood cells (WBCs), and haemoglobin (Hb) % was done. Along with the histological changes in hepatic tissues, genotoxic studies were also carried out. The study showed that profenofos induces different changes in the liver's haematology and histology and nuclear abnormalities in the erythrocytes of treated fish. The results indicate significant differences in RBC and Hb%, whereas marked elevations in WBC count were recorded. The histopathological study of the liver in the treated fish revealed some substantial changes like cell damage, distorted cell shape, vacuolations, etc. Some significant genotoxic effects of profenofos in the erythrocytes were observed, such as the induction of micronuclei, lobed nuclei, irregular-shaped nuclei, notched nuclei, and distorted nuclei. The results were statistically significant at the p < 0.05 level. The study explores the toxic effects of pesticides on the overall health of the fish species. Moreover, the study tried to focus on making decisions about using a tolerable prescribed dose of chemicals to minimize the risk of pesticides. People will also learn that the contamination of the insecticide profenofos is harmful to the aquatic ecosystem, and therefore indiscriminate measures should be avoided.

Aflatoxin (AF) is a toxic metabolite produced by the fungus Aspergillus. The various subtypes of AFs include B1, B2, G1, G2, M1, and M2, with Aflatoxin B1 (AFB1) being the most toxic. These AFs are widespread in the environment, particularly in soil and food crops. The World Health Organization (WHO) has classified AFB1 as a highly potent natural Class 1A carcinogen. Excessive exposure to AFB1 can lead to poisoning in both humans and animals, posing substantial risks to food safety and livestock breeding industries. This review provides an overview of the metabolic processes, detection methods, and the detrimental impacts of AFB1 on animal reproduction, immunity, nerves, intestines, and metabolism. Furthermore, it explores the preventive and control capacities of natural active substances, trace elements, and microorganisms against AFB1. Ultimately, this paper serves as a reference for further research on the pathogenic mechanism of AFB1, the development of preventive drugs, and the selection of effective detoxification measures for AFB1 in animal feed.

As the demand for fish increases, the amount of wastewater generated from fishponds is also increasing with potential environmental and public health effects from their indiscriminate disposal. This study aimed at comparative analyses of the physicochemical and heavy metal constituents and potential DNA damage by wastewaters from natural and artificial fishponds using Allium cepa assay. A. cepa were grown on 3.13, 6.25, 12.5, 25.0, and 50.0% (v/v; wastewater/tap water) concentrations of each wastewater. At 48 and 72 h, respectively, genotoxic and root growth inhibition analyses were carried out on the exposed onions. The onion root tips exposed to wastewaters showed a significant (P < 0.05) inhibition of root growth and cell division in a concentration-dependent manner. Additionally, chromosomal abnormalities like spindle disturbances, sticky chromosomes, micronucleus, bridges, and binucleated cells were observed in the exposed onions and their induction was higher significantly relative to the negative control. Generally, wastewater from the natural fishpond caused higher chromosomal aberrations than the wastewater from artificial fishpond. It is our belief that the cytotoxicity and genotoxicity observed in the onions were primarily caused by heavy metals like Cr, Cd, Fe, Pb, Cu, and Zn found in the wastewaters. These metals also showed a significant carcinogenic and non-carcinogenic risks in children and adults with Cd as the highest contributor to these detrimental risks. Ingestion route was the major exposure route to the toxic metals in these wastewaters. Wastewater from the natural fishpond showed a higher health risk than the wastewater from the artificial fishpond. These findings suggest that the wastewaters from natural and artificial fishpond contain compounds that might induce cytogenotoxicity in exposed organisms.

Background Reactive Red (RR) 141 dye is widely used in various industrial applications, but its environmental impact remains a growing concern. In this study, the phytotoxic and genotoxic effects of RR 141 dye on mung bean seedlings (Vigna radiata (L.) Wilczek) were investigated, serving as a model for potential harm to plant systems.Methods and results Short-term (14 days) and long-term (60 days) experiments in paddy soil pot culture exposed mung bean seedlings to RR 141 dye. The dye delayed germination and hindered growth, significantly reducing germination percentage and seedling vigor index (SVI) at concentrations of 50 and 100 ml/L. In short-term exposure, plumule and radical lengths dose-dependently decreased, while long-term exposure affected plant length and grain weight, leaving pod-related parameters unaffected. To evaluate genotoxicity, high annealing temperature-random amplified polymorphic DNA (HAT-RAPD) analysis was employed with five RAPD primers having 58-75% GC content. It detected polymorphic band patterns, generating 116 bands (433 to 2857 bp) in plant leaves exposed to the dye. Polymorphisms indicated the appearance/disappearance of DNA bands in both concentrations, with decreased genomic template stability (GTS) values suggesting DNA damage and mutation.Conclusion These findings demonstrate that RR 141 dye has a significant impact on genomic template stability (GTS) and exhibits phytotoxic and genotoxic responses in mung bean seedlings. This research underscores the potential of RR 141 dye to act as a harmful agent within plant model systems, highlighting the need for further assessment of its environmental implications.

There has been a growing concern on the health effect of edible plants growing near/on/within the vicinity of dumpsites. This study investigated two edible vegetables: Amarathus hybridus and Talinum triangulare (Jacq) grown in the vicinity of a major informal dumpsite of electronic waste in Nigeria. The levels of polyaromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), and heavy metal concentrations in the vegetables were measured. The health risks of consuming the vegetables were assessed using the hazard index (HI), lifetime cancer risk (LCR), estimated daily intake (EDI), and hazard quotient (HQ). Using the Ames Salmonella fluctuation test on Salmonella typhimurium (TA100 and TA98) and the SOS chromo test on Escherichia coli (PQ37), the mutagenicity and genotoxicity of the vegetables were evaluated. The two vegetables have elevated levels of heavy metals, PBDEs, PCBs, and hazardous PAHs. Compared to A. hybridus, , T. triangulare was more contaminated. The amounts of organic constituents and heavy metals in the vegetables correlated favorably. The levels of the HQ, HI, and LCR were above the suggested guideline values, indicating a significant risk of both carcinogenic and non-carcinogenic consequences, particularly in children. The two vegetables were mutagenic even at 50 % concentration in the Ames test. This was corroborated with SOS-chromo test results showing that the two vegetables were indeed genotoxic. This study demonstrated the harmful effects of growing food crops close to dumpsites; therefore, sufficient measures should be implemented to stop farmers and individuals from utilizing dirt from dumps as fertilizer or from planting in soil that has been used as a dump in the past or present.

The waste generated from cement manufacturing is an important source of heavy metal contamination of groundwater and soil. This study investigated the concentration of toxic metals in the soil of a major cement factory and nearby groundwater. Ecological and carcinogenic risks of the metals were calculated. Potential reproductive toxicity and genotoxic effects of the samples were assessed in the sex and somatic cells of male mice using sperm abnormalities and bone marrow micronucleus (MN) assays, respectively. Also, the serum ALP, ALT, AST, total testosterone (TT), luteinizing hormone (LH), and follicle-stimulating hormone (FSH); and liver SOD and CAT activities were measured in the treated mice. Cr, Cu, Ni, Zn, Mn, Cd, and Pb levels in the soil and groundwater exceeded the allowable maximum standard. Ingestion and dermal contact were the most probable routes of human exposure with children having about 3 times higher probability of exposure to the metals than adults. Ni, Pb, and Cr presented carcinogenic risks in children and adults. In the MN result, nuclear abnormalities in the studied mice especially micronucleated polychromatic erythrocytes increased significantly (P < 0.05). Compared to the negative control, the ratio of PCE/NCE showed the cytotoxicity of the 2 samples. Data further showed a significant increase in the serum ALP, AST, and ALT while the liver CAT and SOD activities concomitantly decreased in the exposed mice. Sperm morphology results showed that the samples contained constituents capable of inducing reproductive toxicity in exposed organisms, with alterations to the concentrations of TT, LH, and FSH. Toxic metal constituents of the samples were believed to induce these reported reproductive toxicity and genotoxic effects. These results showed the environmental pollution caused by cement factories and the potential effects the pollutants might have on exposed eukaryotic organisms.

Global water scarcity entailed the use of treated wastewater (TWW) in agriculture, however, this water can vehiculate numerous pollutants into soil and further crops such as microplastics (MPs). To date, few studies had quantified the accumulation of MPs in soils and earthworms after irrigation with TWW as well as their toxicological effects. Hence, the main objective of the present work is to evaluate the toxicity of MPs using Lumbricus sp. earthworms collected from TWW irrigated soils with an increasing gradient of time (5 years, 16 years and 24 years). MPs determination in soil, as well as in earthworms were performed. The intestinal mucus was quantified, and cytotoxicity (Lysosomal membrane stability (LMS), Catalase (CAT) and glutathione-S-Transferase (GST) activities), neurotoxicity (Acetylcholinesterase activity (AChE)) and genotoxicity (Micronuclei frequency (MNi)) biomarker were assessed. Our results revealed that the use of TWW rendered MPs accumulation in earthworms' tissues and induce alteration on the intestinal mucus. An important cytotoxicity time-depending was observed being associated with an increase on genotoxicity. Overall, the present investigation highlights the ecotoxicological risk associated with the use of TWWs as an important driver of MPs and consequently measures are necessary to reduce MPs in wastewater treatment plans to improve this non-conventional water quality.

Pesticides including insecticides are applied in agricultural practices to control insect pests. However, their excessive usage often poses a severe threat to the growth, physiology, and biochemistry of plants. Here, responses of chickpea and greengram seedlings exposed to three fipronil (FIP) concentrations i. e. 100 (1x), 200 (2x) and 300 (3x) mu g mL- 1 was evaluated under in vitro. Among doses, 3x had a greater negative impact on germination attributes, root-shoot elongation, vigor indices, length ratios, and survival of seedlings. Besides, the morphological distortion in root tips, oxidative stress generation, and cellular death in fipronil-supplemented root seedlings were observed under scanning electron (SEM) and confocal laser scanning (CLSM), respectively. A significant (p <= 0.05) and pronounced upsurge in plant stressor metabolites such as proline, malondialdehyde (MDA), electrolyte leakage (EL), hydrogen peroxide (H2O2) content, and antioxidants enzymes in plant seedlings further confirmed the fipronil toxicity. In addition, a concentration-dependent decrease in respiration efficiency (RE) and ATP content in FIP-treated seedlings was observed. Reduced mitotic index (MI) and numerous chromosomal anomalies (CAs) in root meristematic cells of seedlings are a clear indication of insecticide-induced cytotoxicity. Furthermore, a dose-dependent increase in DNA damage in root meristematic cells of greengram revealed the genotoxic potential of fipronil. Conclusively, fipronil suggested phyto and cyto-genotoxic effects that emphasize their careful monitoring in soils before application and their optimum addition in soil-plant systems. It is high time to prepare both target-specific and slow-released agrochemical formulations for crop protection with concurrent safeguarding of the soil.

Background and aimsMicrobial arsenic (As) methylation in paddy soil produces dimethylarsinic acid (DMA) as the main product, which can cause rice (Oryza sativa L.) straighthead disease characterized by floret sterility. The mode of DMA toxicity remains unclear.MethodsPot and hydroponic experiments were conducted to investigate the effect of DMA and Silicon (Si) additions on floral development, genotoxicity and transcriptomic changes in rice reproductive organs.ResultsDMA preferentially accumulated in rice spikelets and induced floral abnormality. Male fertility was reduced with lower pollen viability due to abnormal degeneration of tapetum under DMA stress. DMA also caused embryo sac defects including degenerated embryo sacs, unusual double ovules, and ovule-free ovaries, which impeded fertilization and reduced seed-setting. Terminal deoxynucleotidyl transferase-mediated dUTP nick-end labeling (TUNEL) and Comet assays showed that DMA accumulation led to DNA damage in the tapetum cells and embryo sacs. Expression of genes related to tapetum development, cell wall formation, and starch synthesis in anthers were frequently affected by DMA. Transcription of genes involved in carbohydrate metabolism in husks and ovaries were altered by DMA stress. Genes related to the DNA damage response and repair were also responsive to DMA stress. Si alleviated DMA toxicity by suppressing DMA accumulation in reproductive tissues.ConclusionsDMA induces genotoxicity in rice reproductive tissue and causes male and female sterility. DMA alters expression of genes associated with tapetum development, carbohydrate metabolism and DNA damage response. The strong genotoxic effect of DMA can be alleviated by supply of Si to rice plants.