首页> 外文期刊>Environmental toxicology and chemistry >RESPONSE AND RECOVERY OF THE MACROPHYTES ELODEA CANADENSIS AND MYRIOPHYLLUM SPICATUM FOLLOWING A PULSE EXPOSURE TO THE HERBICIDE IOFENSULFURON-SODIUM IN OUTDOOR STREAM MESOCOSMS
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RESPONSE AND RECOVERY OF THE MACROPHYTES ELODEA CANADENSIS AND MYRIOPHYLLUM SPICATUM FOLLOWING A PULSE EXPOSURE TO THE HERBICIDE IOFENSULFURON-SODIUM IN OUTDOOR STREAM MESOCOSMS

机译:脉冲暴露于除草剂碘苯磺隆-钠在室外流潮中后,加拿大大叶蝉(Macrophytes Elodea canaddensis)和桃金娘(Smyophyllum SPICATUM)的响应和恢复

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Interest in stream mesocosms has recently revived for higher tier aquatic macrophyte risk assessment of plant protection products mainly because 1) the highest predicted environmental concentrations for the assessment of effects are frequently derived from stream scenarios, and 2) they allow an effect assessment using stream-typical pulse exposures. Therefore, the present stream mesocosm study used an herbicide pulse exposure and evaluated the responses of Elodea canadensis and Myriophyllum spicatum. Macrophytes were exposed for 24h to 1g/L, 3g/L, 10g/L, and 30g/L of the herbicide iofensulfuron-sodium with a subsequent recovery period of 42d. Biological endpoints were growth rates of the main, side, and total shoot length, the shoot number, the maximum root length, and the dry weight. The total shoot length was identified as the most sensitive endpoint; the growth rate of the total shoot length was inhibited by up to 66% and 45% in M. spicatum and E. canadensis, respectively. The lowest no observed effect concentrations (NOECs) were observed at day 7 and/or day 14 after herbicide treatment and were 1g/L for M. spicatum and 3g/L for E. canadensis. The no-observed-ecologically-adverse-effect concentrations (NOEAECs) were 10g/L and 30g/L for M. spicatum and E. canadensis, respectively. Such or similar mesocosm designs are useful to simulate typical stream exposures and estimate herbicide effects on aquatic macrophytes in stream systems. (C) 2016 SETAC
机译:最近,人们对溪流中生环境的兴趣重新开始,用于对植物保护产品进行更高级别的水生植物风险评估,主要是因为1)评估效果的最高预测环境浓度通常来自溪流场景,以及2)它们允许使用溪流进行效果评估。典型的脉冲曝光。因此,目前的流中膜研究使用除草剂脉冲暴露,并评估了加拿大伊乐藻和桃金娘的响应。将大型植物暴露于1g / L,3g / L,10g / L和30g / L除草剂碘芬磺隆钠的24小时,随后的恢复期为42天。生物终点是主茎,侧枝和总芽长,芽数,最大根长和干重的生长率。总的芽长被确定为最敏感的终点。辣根分枝杆菌和加拿大E. canadensis的总芽长生长率分别被抑制高达66%和45%。在除草剂处理后的第7天和/或第14天,观察到的最低无效应浓度(NOEC)最低,对穗状分枝杆菌为1g / L,对加拿大大肠埃希菌为3g / L。观察到的M. spicatum和E. canadensis的未观察到的生态不利影响浓度(NOEAECs)分别为10g / L和30g / L。这种或类似的中观宇宙观设计可用于模拟典型的河流暴露并估算除草剂对河流系统中水生植物的影响。 (C)2016年SETAC

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