USC1233 INRA-VetAgro-Sup Campus Vétérinaire de Lyon, 1 avenue Bourgelat, 69280 Marcy l'Etoile, France.
ACTA, ICB-VetAgro-Sup, 1 avenue Bourgelat, 69280 Marcy l'étoile, France.
Sci Total Environ. 2018 Jan 1;610-611:576-582. doi: 10.1016/j.scitotenv.2017.08.117. Epub 2017 Aug 17.
Anticoagulant rodenticides (ARs) are used worldwide to control populations of agricultural and urban rodents, but these pesticides may be accumulated in and poisoned non-target species of wildlife. Slugs may feed on rodenticide bait following field applications. Thus, it can be assumed that their predators are exposed to rodenticides through food chain transfer. However, AR exposure in the slugs has not been systematically studied. We investigated the accumulation of three ARs (chlorophacinone, bromadiolone or brodifacoum) in the slug Deroceras reticulatum exposed for a period of 5days followed by depuration time of 4days in the laboratory. Moreover, we studied the exposure of slugs to brodifacoum in the field. In the laboratory exposure, the slugs consumed rodenticide baits, but no mortality was observed. After 1day, their concentrations were stable over the time and no differences were detected between the concentrations of the three ARs. After 5days of exposure, mean concentrations in slugs were 1.71, 1.91 and 0.44mg/kg wet weight for chlorophacinone, bromadiolone and brodifacoum respectively. A significant decrease of bromadiolone and brodifacoum in slugs was observed in the post exposure period. In the field study, brodifacoum was detected in >90% of analyzed slugs after application of brodifacoum baits. Then, based on a toxicity-exposure ratio approach, we found that slug consumption may represent a risk of secondary poisoning for three of their predators under acute, repeated or subchronic exposure scenarios. These results suggest that the slugs are not only the potential subject to primary exposure, but also the source of secondary exposure for their predators following application of rodenticide baits.
抗凝血灭鼠剂(ARs)在全球范围内用于控制农业和城市啮齿动物的数量,但这些杀虫剂可能在非目标野生动物物种中积累和中毒。鼻涕虫可能会在田间应用后食用灭鼠诱饵。因此,可以假设它们的捕食者通过食物链转移接触到灭鼠剂。然而,鼻涕虫对 AR 的暴露情况尚未得到系统研究。我们研究了三种 AR(氯鼠酮、溴敌隆或溴鼠灵)在实验室中暴露 5 天后并在接下来的 4 天内进行清除时间后,在食蜗螺 Deroceras reticulatum 中的积累情况。此外,我们还研究了食蜗螺在野外接触溴鼠灵的情况。在实验室暴露中,鼻涕虫食用了灭鼠诱饵,但未观察到死亡。第 1 天,它们的浓度随时间稳定,三种 AR 的浓度没有差异。暴露 5 天后,食蜗螺中氯鼠酮、溴敌隆和溴鼠灵的平均浓度分别为 1.71、1.91 和 0.44mg/kg 湿重。暴露后期间,溴敌隆和溴鼠灵在鼻涕虫中的浓度显著下降。在野外研究中,在应用溴敌隆诱饵后,>90%的分析鼻涕虫中检测到溴敌隆。然后,基于毒性-暴露比方法,我们发现,在急性、重复或亚慢性暴露情景下,鼻涕虫的消耗可能代表其三种捕食者发生二次中毒的风险。这些结果表明,鼻涕虫不仅是原发性暴露的潜在对象,而且在灭鼠剂诱饵应用后,也是其捕食者发生继发性暴露的来源。