The fate of fenitrothion in rice- fish ecosystem was studied using C- fenitrothion (14C- F) labelled at methoxyl and two application rates. The fenitrothion in water disappeared quickly, only 8 and 11 ppb in two treat...The fate of fenitrothion in rice- fish ecosystem was studied using C- fenitrothion (14C- F) labelled at methoxyl and two application rates. The fenitrothion in water disappeared quickly, only 8 and 11 ppb in two treatments at harvest were detected respectively. Most of 14C-F in soil existed in upper layer and that in plants appeared in shoots. The extractable residues in cargo rice were 0.36 and 0.58 ppm in two treatments respectively. 14C- residues (14C- R) were concentrated in bones, next viscera, meat and scales. Total 14C-R in meat were 0.92 and 1.77 ppm at harvest. Comparing two treatments, the residue dynamics of fenitrothion in water, soil, plants and fish were similar. 14C- R in water and soil after harvest affected the rice- fish ecosystem in the next season. However, the extractable 14C- R in cargo rice, soil and water were very low. Fenitrothion 14C- fenitrothion Rice- fish Model展开更多
为了研究低剂量杀螟硫磷(fenitrothion-O-analog,FNT)暴露对大鼠肝细胞(buffalo rat liver cells,BRL)的代谢毒性,并通过作用于体外的一系列指标分析其作用机制,分别对空白对照组和杀螟硫磷暴露组(13.78、27.55、55.10μg·mL-1)暴...为了研究低剂量杀螟硫磷(fenitrothion-O-analog,FNT)暴露对大鼠肝细胞(buffalo rat liver cells,BRL)的代谢毒性,并通过作用于体外的一系列指标分析其作用机制,分别对空白对照组和杀螟硫磷暴露组(13.78、27.55、55.10μg·mL-1)暴露48 h,观察其对BRL内糖代谢、胰岛素敏感和糖原合成信号通路中蛋白表达的影响。实验结果表明,杀螟硫磷暴露能够显著抑制BRL细胞的活力,半数抑制浓度(IC50)为275.5μg·mL-1。杀螟硫磷暴露使超氧化物歧化酶(superoxide dismutase,SOD)和乙酰胆碱酯酶AchE活力显著降低(P<0.01),其体内丙二醛(malonaldehyde,MDA)含量显著增加(P<0.01),引起细胞氧化损伤。杀螟硫磷暴露使其细胞内糖原、胰岛素和葡萄糖激酶含量显著降低(P<0.01),增加胰岛素抵抗。杀螟硫磷暴露显著下调胰岛素敏感信号通路中IRS的表达,抑制IRS的磷酸化,并显著上调AKT和PI3K的表达,显著上调糖原合成信号通路中GSK-3α和GSK-3β的表达。因此,杀螟硫磷暴露使BRL产生糖代谢毒性的机制是通过氧化应激诱发胰岛素抵抗,从而改变糖代谢相关信号通路中蛋白的表达而实现的。展开更多
文摘The fate of fenitrothion in rice- fish ecosystem was studied using C- fenitrothion (14C- F) labelled at methoxyl and two application rates. The fenitrothion in water disappeared quickly, only 8 and 11 ppb in two treatments at harvest were detected respectively. Most of 14C-F in soil existed in upper layer and that in plants appeared in shoots. The extractable residues in cargo rice were 0.36 and 0.58 ppm in two treatments respectively. 14C- residues (14C- R) were concentrated in bones, next viscera, meat and scales. Total 14C-R in meat were 0.92 and 1.77 ppm at harvest. Comparing two treatments, the residue dynamics of fenitrothion in water, soil, plants and fish were similar. 14C- R in water and soil after harvest affected the rice- fish ecosystem in the next season. However, the extractable 14C- R in cargo rice, soil and water were very low. Fenitrothion 14C- fenitrothion Rice- fish Model