Umweltbundesamt, Schichauweg 58, 12307 Berlin, Germany.
Aquat Toxicol. 2012 Oct 15;122-123:56-66. doi: 10.1016/j.aquatox.2012.05.012. Epub 2012 Jun 2.
Pesticide contaminations via run-off or spray drift have been reported to result in the mass drift of macroinvertebrates as well as causing structural and functional changes of the corresponding stream sections. However, pesticide pulses in the field are associated with sudden increases in flow velocity, water turbidity, and changes in water temperature, which can also induce drift. Only through replicated community testing under highly controlled conditions can these effects be disentangled. In a stream mesocosm study, 12-h pulses of 12 μg/L imidacloprid were set three times at weekly intervals and are considered a "pulse series". Two pulse series of this neonicotinoid insecticide were run in both spring and summer with 4 treatment and 4 control stream mesocosms used in each pulse series. Prior to the start of the mesocosm experiment, both pulse concentration and duration had been screened for drift responses in larval Baetidae, Chironomidae and adult Gammarus roeseli in laboratory experiments. In the subsequent mesocosm study, each pulse caused a pronounced increase in the drift of insect larvae and gammarids. The drift response was taxon-specific, which was related to preferred habitat and exposure to other stressors like current velocity, in addition to imidacloprid sensitivity. Activity measurements employing a Multispecies Freshwater Biomonitor(®) revealed that in Baetis sp. the diurnal activity pattern became more pronounced even 12h after the pulse though with slightly decreased mean physical activity. Adult G. roeseli showed a drastic pulse by pulse decrease in physical activity which after the 3rd pulse lasted longer than 24h. In conclusion, drift is a sensitive, ecologically relevant endpoint and should be regarded when a specific risk assessment for lotic surface waters is done, e.g. in the context of a spatially explicit risk assessment.
已有报道称,由于径流或喷雾漂移,农药污染会导致大型无脊椎动物大量漂移,并导致相应溪流段的结构和功能发生变化。然而,田间农药脉冲与流速、水浊度和水温变化的突然增加有关,这些变化也会引起漂移。只有在高度受控的条件下进行重复的群落测试,才能将这些影响区分开来。在溪流中观模拟研究中,每周设置三次持续 12 小时、浓度为 12μg/L 的吡虫啉脉冲,这被认为是一个“脉冲系列”。在春季和夏季进行了两次该新烟碱类杀虫剂的脉冲系列实验,每个脉冲系列使用 4 个处理和 4 个对照溪流中观模拟。在中观模拟实验开始之前,已经在实验室实验中筛选了幼虫蜉蝣目、摇蚊目和成年罗氏沼虾对吡虫啉的脉冲浓度和持续时间的漂移反应。在随后的中观模拟研究中,每个脉冲都会导致昆虫幼虫和桡足类的明显漂移增加。漂移反应具有分类群特异性,这与首选栖息地以及对其他胁迫因素(如流速)的暴露有关,而不是与吡虫啉敏感性有关。使用多物种淡水生物监测仪进行的活动测量显示,在蜉蝣目中,即使在脉冲后 12 小时,昼夜活动模式也变得更加明显,尽管平均体力活动略有下降。成年罗氏沼虾的体力活动在每个脉冲中急剧下降,第 3 个脉冲后的持续时间超过 24 小时。总之,漂移是一个敏感的、具有生态相关性的终点,在对流水表面水进行特定风险评估时应加以考虑,例如在空间明确的风险评估背景下。