甲氨基阿维菌素苯甲酸盐和多杀霉素纳米制剂对蜜蜂和蚯蚓的急性毒性与初级风险评估

    Acute toxicity and primary risk assessment of nano-formulations of emamectin benzoate and spinosad on Apis mellifera and Eisenia foetida

    • 摘要: 为探明纳米化剂型对非靶标生物的毒性影响,本研究选取甲氨基阿维菌素苯甲酸盐和多杀霉素,通过开展同期试验,对比分析了原药、纳米制剂以及常规剂型对照药剂对蜜蜂和蚯蚓的急性毒性与风险。结果表明:1)以毒性系数 (TF) 表示制剂与原药相比的毒性变化,所得纳米制剂的TF值均≤4.2,对照药剂TF值最高为9.0,即2种纳米制剂对蜜蜂和蚯蚓的毒性波动范围未超出对照常规剂型药剂的毒性波动范围。2)甲氨基阿维菌素苯甲酸盐II型纳米制剂对蚯蚓的急性毒性 (LC50 = 36.4 mg a.i./kg (soil)) 低至对照药剂乳油 (LC50 = 2.4 mg a.i./kg (soil)) 的约1/15;多杀霉素I型纳米制剂对蜜蜂的急性经口毒性 (LD50 = 0.124 µg a.i./bee) 为对照悬浮剂 (LD50 = 0.234 µg a.i./bee) 的1.9倍,接触毒性 (LD50 = 0.019 µg a.i./bee) 则仅为对照药剂 (LD50 = 0.003 µg a.i./bee) 的约1/6。分析产生上述差异的可能原因在于制剂配方与剂型特性,以及受试生物类型及暴露途径 (经口或接触) 的不同。纳米农药对非靶标生物的风险是其有效成分固有毒性、剂型配方组分、纳米特征及其稳定性、环境行为及暴露场景的复合函数,建议现阶段针对纳米农药的环境安全评价宜采用“个案分析”策略,未来需开展广泛研究积累数据、探寻规律,针对性构建纳米农药对非靶标生物的风险评估合理方法。

       

      Abstract: To investigate the toxic effects of nano-formulations on non-target organisms, this study selected abamectin benzoate and spinosad to compare the acute toxicity and risk of their active ingredients, nano-formulations, and conventional formulations toward Apis mellifera and Eisenia foetida. The results showed: first, the toxicity factor (TF), representing the toxicity change of a formulation relative to active ingredient, was used as an indicator. The TF values for both nano-formulations were ≤4.2, whereas the conventional formulation had the highest TF value of 9.0. This indicates that the toxicity fluctuations of the two nano-formulations did not exceed those of the conventional controls. Second, the acute toxicity of the nanoformulation of abamectin benzoate type II to E. foetida (LC50 = 36.4 mg a.i./kg (soil)) was approximately 1/15 that of the reference emulsifiable concentrate (LC50 = 2.4 mg a.i./kg (soil)). For spinosad type I nanoformulation, the acute oral toxicity toward A. mellifera (LD50 = 0.124 µg a.i./bee) was 1.9 times greater than that of the control suspension concentrate (LD50 = 0.234 µg a.i./bee), whereas its contact toxicity (LD50 = 0.019 µg a.i./bee) was only about one-sixth of the control (LD50 = 0.003 µg a.i./bee). These differences may be attributed to formulation composition, physicochemical properties, test organism species, and exposure routes (oral or contact). The environmental risk of nanopesticides to non-target organisms is a complex function of the inherent toxicity of their active ingredients, formulation components, nano-characteristics, stability, environmental behavior, and exposure scenarios. Therefore, a "case-by-case" approach is recommended for the environmental safety assessments of nanopesticides. Future research should focus on data accumulation and pattern identification to develop rational and targeted methods for the risk assessment of nanopesticides.

       

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