草甘膦和苯甲酸乙酯类杀虫剂对淡水大对虾幼体的生物影响

IF 4.3 3区 材料科学 Q1 ENGINEERING, ELECTRICAL & ELECTRONIC
Arsène Mathieu Houssou, Togbéadji Fabrice Lokonon, Guillaume Koussovi, Dogbè Clément Adjahouinou, Daniel Cocan, Elie Montchowui
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引用次数: 0

摘要

在发展中国家,以苯甲酰甲胺磷为基础的杀虫剂和以草甘膦为基础的除草剂被广泛用于农业目的。问题在于完全缺乏有关其用途的数据知识,也缺乏有关其对当地生物多样性潜在影响的科学数据。本研究评估了 EMACOT® 和 SUNPHOSATE-G® 两种商业制剂对贝宁大流域原生对虾(Macrobrachium macrobrachion)幼体的急性和慢性影响。对平均体重为 1.49 ± 0.2 克的幼体分别施用了六次和七次致死剂量的 EMACOT® 和 SUNPHOSAT-G®。然后,对单独暴露于标称浓度为 0.06 和 0.11 mg.L-1 的 EMACOT 以及 13.99 和 27.98 mg.L-1 的 SUNPHOSATHE-G 的幼鱼的蜕皮效果、体重和体型增长以及存活率的亚致死效应进行了评估。结果表明,除草剂配方对幼鱼的 LC50-72 小时浓度为 279.76 mg.L-1,相当于草甘膦的 211.78 mg.L-1。杀虫剂的半数致死浓度为 1.14 毫克/升,相当于 0.06 毫克/升的甲胺基苯甲酸酯。至于慢性影响,两种浓度的苯甲酸阿维菌素都会阻止对虾蜕皮(实验开始时对虾蜕皮 1 次,而对照组在 28 天内蜕皮 3 次)。因此,这两种处理的增重非常低(分别为 0.06 克和 0.19 克),而对照组的增重为 0.66 克。对于草甘膦,13.99 毫克/升-1 的研究结果与两种剂量的苯甲酸依马霉素相似。另一方面,在 27.98 mg.L-1 处理(28 天内蜕皮 3 次)中,未观察到对蜕皮效果的显著影响。草甘膦亚致死剂量和草甘膦亚致死剂量的增重分别为 0.11 克和 0.46 克。该研究结果表明,对虾幼体对阿维菌素苯甲酸盐(EMACOT)非常敏感,而对草甘膦(SUNPHOSATE-G)的敏感性相对较低。但是,如果在大河的洪泛平原使用这两种杀虫剂,风险就会很大。在贝宁等发展中国家,必须采取措施审查目前在大流域使用杀虫剂的做法。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Biological effects of glyphosate and emamectin benzoate based pesticides on the freshwater prawn Macrobrachium macrobrachion juveniles

Biological effects of glyphosate and emamectin benzoate based pesticides on the freshwater prawn Macrobrachium macrobrachion juveniles

Emamectin benzoate based insecticide and glyphosate based herbicides are widely used in developing countries for agricultural purposes. The problem lies in the total lack of knowledge of data on their uses as well as the absence of scientific data on the potential effects on local biodiversity. This study evaluates the acute and chronic effects of two commercial formulations EMACOT® and SUNPHOSATE-G® on juveniles of a prawn species (Macrobrachium macrobrachion) native of large watersheds in Benin. Juveniles with an average weight of 1.49 ± 0.2 g were subjected to six and seven lethal doses of EMACOT® and SUNPHOSAT-G® respectively. Thus, swimming behavior, loss of mobility and mortality were monitored every hour for 72 h. Then, sub-lethal effects on molting effectiveness, weight and size gain as well as survival were evaluated on juveniles individually exposed to nominal concentrations of 0.06 and 0.11 mg.L-1 of EMACOT, and 13.99 and 27.98 mg.L-1 of SUNPHOSATHE-G. The results showed that the LC50-72 h of the herbicide formulation on juveniles is 279.76 mg.L-1 which corresponds to 211.78 mg.L-1 of glyphosate. That of the insecticide is 1.14 mg.L-1 corresponding to 0.06 mg.L-1of emamectin benzoate. As for the chronic effects, both concentrations of emamectin benzoate prevented the prawn from molting (1 molt at the start of the experiment against 3 molts for the control subjects in 28 days). As a result, weight gain in these two treatments was very low (0.06 and 0.19 g, respectively) compared to 0.66 g in the controls. For glyphosate, findings with 13.99 mg.L-1 are similar to those of both doses of emamecin benzoate. On the other hand, no significant effect was observed on the effectiveness of molts within 27.98 mg.L-1 treatment (3 molts in 28 days). The weight gain was 0.11 g and 0.46 g respectively for both glyphosate sub-lethal doses. The results of this study indicate a significant sensitivity of the prawn juveniles to emamectin benzoate (EMACOT) and a relatively low sensitivity to glyphosate (SUNPHOSATE-G). But the risk is significant when these two pesticides are used in the flood plains of large rivers. In developing countries such as Benin, measures must be taken to review current pesticide use practices in large watersheds.

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