首页> 外文期刊>Environmental toxicology and chemistry >ICON~(~R) RICE SEED TREATMENT TOXICITY TO CRAYFISH (PROCAMBARUS CLARKII) IN EXPERIMENTAL RICE PADDIES
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ICON~(~R) RICE SEED TREATMENT TOXICITY TO CRAYFISH (PROCAMBARUS CLARKII) IN EXPERIMENTAL RICE PADDIES

机译:ICON〜(〜R)大米对实验性稻米对小龙虾(小螯虾)的处理毒性

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Outdoor pools (2.3 X 2.3 m) were used to simulate typical rice agricultural practices in Louisiana, USA, to evaluate the toxicity of ICON~(~R) (active ingredient [a.i.] fipronil) and its degradates to crayfish (Procambarus clarkii). Six paddies were planted with seed treated with ICON 6.2 FS at an exaggerated application rate of 0.05 kg a.i./ha (recommended rate, 0.042 kg a.i./ ha), simulating three rice-planting scenarios. Two reference paddies were planted with untreated seed. Crayfish were exposed to tail water within 24 to 48 h after seeding, simulating standard Louisiana agricultural and water management practices. At 50 d after planting, a separate group of crayfish was caged in situ for 14 d to evaluate toxicity. An additional 50 crayfish were added to two paddies approximately 100 d after rice planting and held for 29 weeks to evaluate bioaccumulation. Residues of fipronil and its degradates in water and soil were similar to residue concentrations measured from rice fields in Louisiana. Tail water from the treated paddies was not toxic to crayfish. The fipronil 96-h median lethal concentration (LC50) for adult crayfish was 180 μg/ L, which would provide at least a sixfold safety factor between the maximum fipronil concentration in tail water and the crayfish LC50. In situ exposures of crayfish also were not toxic. Concentrations of fipronil and its degradates after 29 weeks of exposure were less than 5 μg/kg in crayfish tail muscle tissue. These results demonstrate that label instructions adequately protect crayfish in a rice-crayfish cropping scenario when ICON is applied at maximum application rates as a seed treatment.
机译:在美国路易斯安那州,使用室外游泳池(2.3 X 2.3 m)来模拟典型的水稻种植实践,以评估ICON〜(〜R)(活性成分氟虫腈)的毒性及其降解为小龙虾(Procambarus clarkii)的能力。模拟了三种水稻种植情况,以六种稻田播种了用ICON 6.2 FS处理过的种子,夸大的施用量为0.05 kg a.i./ha(建议施用量为0.042 kg a.i./ha)。两个参考水稻种植未经处理的种子。小龙虾在播种后24至48小时内暴露于尾水,模拟路易斯安那州的标准农业和水管理实践。种植后第50天,将另一组小龙虾原地关笼14天,以评估毒性。水稻种植大约100天后,将另外50个小龙虾添加到两个水稻中,并保持29周以评估生物蓄积性。氟虫腈及其在水和土壤中降解的残留物与路易斯安那州稻田中测得的残留物浓度相似。处理过的稻田中的尾水对小龙虾无毒。成年小龙虾的氟虫腈96小时平均致死浓度(LC50)为180μg/ L,这将在尾水中的最大氟虫腈浓度和小龙虾LC50之间提供至少六倍的安全系数。小龙虾的原位暴露也没有毒性。暴露29周后,小龙虾尾部肌肉组织中氟虫腈及其降解物的浓度低于5μg/ kg。这些结果表明,当以最大施用量施用ICON作为种子处理剂时,标签说明可在水稻小龙虾种植中充分保护小龙虾。

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