Fosthiazate exposure induces oxidative stress, nerve damage, and reproductive disorders in nontarget nematodes

Diquat Induces Cell Death and dopamine Neuron Loss via Reactive Oxygen Species Generation in Caenorhabditis elegans

Diquat (DQ), a contact herbicide extensively utilized in both agricultural and nonagricultural domains, exhibits a high correlation with neuronal disorders. Nevertheless, the toxicity and underlying mechanisms associated with exposure to environmental concentrations of DQ remain ambiguous. Here, we report dose-dependent cellular neurotoxicity of DQ in Caenorhabditis elegans. First, DQ significantly compromised the development and brood size of worms, shortened the lifespan, and caused epidermal abnormalities. An unbiased transcriptomic analysis disclosed several pathways related to cell death and peroxisome homeostasis underlying this organismal-level toxicity. Moreover, exposure of DQ to C. elegans led to a notable increase of embryonic cell death. Concurrently, DQ exposure specifically caused the loss of dopamine neurons but not two other types of neurons in adulthood, which is in accordance with DQ-induced muscle-related defects such as pharyngeal pumping, body bends, and head thrashes. Mechanistically, DQ exposure induces the generation of reactive oxygen species (ROS) and enhances glutathione-related ROS scavenging pathway. Protein levels and activities of mitochondrial electron transport chain complexes were specifically impaired in the DQ-treated worms. Collectively, this study suggests an ROS-mediated cell death pathway involving the neuronal and behavioral toxicity of DQ, which offers a novel mitochondria-related perspective to elucidate the general toxicity caused by a widely distributed herbicide, DQ, at near-environment concentrations.

Ecotoxicological risk of co-exposure to fosthiazate and microplastics on earthworms (Eisenia fetida): Integrating biochemical and transcriptomic analyses

Fosthiazate (FOS) is a widely used organophosphorus insecticide effective against soil root-knot nematodes. However, its ecotoxicity to non-target soil organisms, particularly in combination with microplastics (MPs), is unclear. This study explores the toxic-effects and molecular mechanisms of co-exposure to FOS and MPs on earthworms (Eisenia fetida) using multilevel toxicity endpoints and transcriptomics. Results showed that both FOS and MPs elevated the intracellular levels of reactive oxygen species (ROS), malondialdehyde (MDA), and 8-hydroxy-2-deoxyguanosine (8-OHdG) in earthworms' cells. The superoxide dismutase (SOD) and catalase (CAT) activities followed a similar trend in all treatments, with changes observed at 14 and 28 days, indicating that co-exposure to FOS and MPs increased DNA oxidative damage. Notably, the co-exposure more significantly inhibited Ca2+-ATPase activity and exacerbated neurotoxicity compared to individual treatments, closely associated with changes in intracellular ROS levels that mediate neuroinhibition and lead to neurotoxicity. KEGG enrichment analysis revealed that MPs and FOS disrupted pathways related to metabolism, immunity, and apoptosis, while co-exposure primarily impaired endocrine and receptor pathways, showing higher toxicity. Our study offers novel insights into the ecotoxicological effects and mechanisms of pesticides and microplastics on earthworms, providing valuable data for evaluating the soil environmental health risks associated with compound pollution.

Reproductive Toxicity and Multi/Transgenerational Effects of Emerging Pollutants on C. elegans

Emerging pollutants (EPs) are receiving increasing attention due to the threats they pose to the environment and human health. As EPs continue to emerge, risk assessment requires many model animals. Caenorhabditis elegans (C. elegans) has been an outstanding toxicological model organism due to its growth and development characteristics. Particularly, in studying the transgenerational influences of EPs, C. elegans has advantages in saving time and cost due to its short generation cycle. As infertility has become a major problem in human reproductive health, reproductive toxicities of EPs on contemporary nematodes and across generations of C. elegans were introduced in this review. Moreover, the underlying mechanisms involved in germ cell apoptosis, spermatogenesis, and epigenetic alteration were discussed. Future research opportunities and challenges are also discussed to expand our understanding of the reproductive influences of EPs.

Testosterone Mediates Reproductive Toxicity in Caenorhabditis elegans by Affecting Sex Determination in Germ Cells through nhr-69/mpk-1/fog-1/3

Testosterone (T), an environmental androgen, significantly disrupts endocrine systems in wildlife and ecosystems. Despite growing concern over its high levels in aquatic environments, the reproductive toxicity of testosterone and its mechanisms are not well understood. In this study, we investigated the reproductive toxicity and mechanisms of testosterone using Caenorhabditis elegans (C. elegans) and assessed its ecological toxicity through the benchmark dose (BMD) method. Our results indicate that T concentrations exceeding 0.01 μg/L significantly reduce the brood size, decrease germ cell counts, and prolong the generation time in C. elegans as T concentrations increase. Furthermore, to elucidate the specific mechanisms, we analyzed the expression of nhr-69, mpk-1, and other genes involved in sex determination. These findings suggest that the nhr-69-mediated reproductive toxicity of T primarily affects sperm formation and the offspring number by influencing its downstream targets, mpk-1 and fog-1/3, which are critical in the germ cell sex-determining pathway. Additionally, this study determined that the 10% lower boundary of the baseline dose (BMDL10) is 1.160 ng/L, offering a more protective reference dose for the ecological risk assessment of T. The present study suggests that nhr-69 mediates the reproductive toxicity of T by influencing mpk-1 and fog-1/3, critical genes at the end of the germ cell sex-determining pathway, thereby providing a basis for establishing reproductive toxicity thresholds for T.

Vitamin A ameliorates valproic acid-induced autism-like symptoms in developing zebrafish larvae by attenuating oxidative stress and apoptosis

Autism spectrum disorder (ASD) is a neurodevelopmental disorder characterized by social deficits and repetitive/stereotyped behaviors. Prenatal exposure to valproic acid (VPA) has been reported to induce ASD-like symptoms in human and rodents. However, the etiology and pathogenesis of ASD have not been well elucidated. This study aimed to explore the mechanisms underlying VPA-induced ASD-like behaviors using zebrafish model and investigated whether vitamin A could prevent VPA-induced neurotoxicity. Here, zebrafish embryos were exposed to 0, 25 and 50 μM VPA from 4 to 96 h post fertilization (hpf) and the neurotoxicity was assessed. Our results showed that VPA affected the normal development of zebrafish larvae and induced ASD-like behaviors, including reduced locomotor activity, decreased distance near conspecifics, impaired social interaction and repetitive swimming behaviors. Exposure to VPA decreased the GFP signal in transgenic HuC:egfp zebrafish according to the negative effect of VPA on the expression of neurodevelopmental genes. In addition, VPA enhanced oxidative stress by promoting the production of reactive oxygen species (ROS) and hydrogen peroxide (H2O2) and inhibiting the activity of superoxide dismutase, then triggered apoptosis by upregulation of apoptotic genes. These adverse outcomes were mitigated by vitamin A, suggesting that vitamin A rescued VPA-induced ASD-like symptoms by inhibiting oxidative stress and apoptosis. Overall, this study identified vitamin A as a promising strategy for future therapeutic regulator of VPA-induced ASD-like behaviors.

Fosthiazate, a soil-applied nematicide, induces oxidative stress, neurotoxicity and transcriptome aberrations in earthworm (Eisenia fetida)

Fosthiazate is a widely used organophosphorus nematicide that resides in the soil and controls soil root-knot nematodes. However, whether it has toxic effects on non-target soil organisms such as earthworms is unclear. Therefore, in this study, a 28-day experiment of fosthiazate exposure was conducted using the Eisenia fetida as the model organism. The results showed that fosthiazate stress caused excessive production of reactive oxygen species (ROS), increased the levels of malondialdehyde (MDA) and 8-hydroxy-2-deoxyguanosine (8-OHdG), and decreased the activities of superoxide dismutase (SOD) and catalase (CAT), suggesting that fosthiazate induced oxidative stress and DNA damage in E. fetida. Acetylcholinesterase (AChE) activity was significantly reduced, and the expression of its related functional genes was also altered, demonstrating that fosthiazate damaged the nervous system of E. fetida, which was further confirmed by AlphaFold2 modeling and molecular docking simulations. Furthermore, Kyoto Encyclopedia of Genes and Genomes (KEGG) enrichment analysis indicated that fosthiazate exposure may induce apoptosis, inflammation, and viral infection in E. fetida, which adversely affect the organism. This study provides reference data for the ecotoxicity of fosthiazate.

Oxidative stress and mitochondrial damage induced by a novel pesticide fluopimomide in Caenorhabditis elegans

Fluopimomide is a novel pesticide intensively used in agricultural pest control; however, its excessive use may have toxicological effects on non-target organisms. In this study, Caenorhabditis elegans was used to evaluate the toxic effects of fluopimomide and its possible mechanisms. The effects of fluopimomide on the growth, pharyngeal pumping, and antioxidant systems of C. elegans were determined. Furthermore, the gene expression levels associated with mitochondria in the nematodes were also investigated. Results indicated that fluopimomide at 0.2, 1.0, and 5.0 mg/L notably (p < 0.001) decreased body length, pharyngeal pumping, and body bends in the nematodes compared to the untreated control. Additionally, fluopimomide at 0.2, 1.0, and 5.0 mg/L notably (p < 0.05) increased the content of malondialdehyde by 3.30-, 21.24-, and 33.57-fold, respectively, while fluopimomide at 1.0 and 5.0 mg/L significantly (p < 0.001) increased the levels of reactive oxygen species (ROS) by 49.14% and 77.06% compared to the untreated control. In contrast, fluopimomide at 1.0 and 5.0 mg/L notably reduced the activities of target enzyme succinate dehydrogenase and at 5.0 mg/L reduced the activities of antioxidant enzyme superoxide dismutase. Further evidence revealed that fluopimomide at 1.0 and 5.0 mg/L significantly inhibited oxygen consumption and at 0.2, 1.0, and 5.0 mg/L significantly inhibited ATP level in comparison to the untreated control. The expression of genes related to the mitochondrial electron transport chain mev-1 and isp-1 was significantly downregulated. ROS levels in the mev-1 and isp-1 mutants after fluopimomide treatments did not change significantly compared with the untreated mutants, suggesting that mev-1 and isp-1 may play critical roles in the toxicity induced by fluopimomide. Overall, the results demonstrate that oxidative stress and mitochondrial damage may be involved in toxicity of fluopimomide in C. elegans.