Beijing Advanced Innovation Center for Food Nutrition and Human Health, Department of Applied Chemistry, China Agricultural University, Yuanmingyuan West Road 2, Beijing, 100193, China.
Department of Applied Chemistry, China Agricultural University, Yuanmingyuan West Road 2, Beijing, 100193, People's Republic of China.
Environ Sci Pollut Res Int. 2017 Feb;24(4):3618-3625. doi: 10.1007/s11356-016-8128-5. Epub 2016 Nov 24.
Efficacy and potential environmental risks should be considered when applying enantiopure pesticides. In this study, Tubifex tubifex and its oxidative stress biomarkers were assessed for the toxicity of metalaxyl and metalaxyl-M in sediment. The toxicity assessment was conducted with artificial sediment and reconstituted water. Five test concentrations (from 0 to 100 mg/kg) were set for the short-term (4 days) exposure. The long-term (28 days) exposure was conducted with the environmental concentration (from 0.5 to 5 mg/kg). For the short-term exposure, the increase of superoxide dismutase (SOD) activity was observed, and a clear concentration-response relationship was found in the metalaxyl treatments. The decrease of catalase (CAT) and glutathione peroxidase (GPx) activity could be caused by oxidative stress. The decrease of glutathione (GSH) content and the increase of glutathione-S-transferase (GST) might be due to antioxidation defense and detoxification mechanisms. The increase of malondialdehyde (MDA) might be due to the saturation of antioxidant systems and the accumulation and toxicity of contaminations. In the long-term exposure, the changes of biomarkers in T. tubifex reflected the oxidative stress and detoxification metabolisms. GSH and the related enzymes were important in detoxification processes and involved in the oxidative stress in toxicity mechanism. The long-term direct contact bioassay is sensitive and appropriate to reflect the lower concentration of contaminants.
在应用对映体纯农药时,应考虑其功效和潜在的环境风险。本研究评估了金属草隆和金属草隆-M 在沉积物中的毒性对水丝蚓(Tubifex tubifex)及其氧化应激生物标志物的影响。采用人工沉积物和再水合水进行毒性评估。设置了五个测试浓度(0 至 100mg/kg)进行短期(4 天)暴露。采用环境浓度(0.5 至 5mg/kg)进行长期(28 天)暴露。在短期暴露中,观察到超氧化物歧化酶(SOD)活性增加,并且在金属草隆处理中发现了明显的浓度-反应关系。过氧化氢酶(CAT)和谷胱甘肽过氧化物酶(GPx)活性的降低可能是由氧化应激引起的。谷胱甘肽(GSH)含量的降低和谷胱甘肽-S-转移酶(GST)的增加可能是由于抗氧化防御和解毒机制。丙二醛(MDA)的增加可能是由于抗氧化系统的饱和以及污染物的积累和毒性。在长期暴露中,水丝蚓生物标志物的变化反映了氧化应激和解毒代谢。GSH 和相关酶在解毒过程中很重要,并且参与了毒性机制中的氧化应激。长期直接接触生物测定法敏感且适当,能够反映出较低浓度的污染物。