Department of Zoology, University of Cambridge, Downing Street, Cambridge CB2 3EJ, UK.
Ecotoxicol Environ Saf. 2013 Nov;97:183-8. doi: 10.1016/j.ecoenv.2013.08.007. Epub 2013 Sep 2.
When planning rodent eradications, that normally involve the use of the anticoagulant poison brodifacoum, it is imperative to minimise impacts on other "non-target" species that dwell alongside the targeted rodents and may indeed be the intended beneficiaries of the eradication. Such impacts can arise either from primary poisoning when the non-target species ingest bait pellets containing toxicant or by secondary poisoning when the non-target species eats prey that has itself eaten brodifacoum. Cockroaches and woodlice, likely to scavenge bait pellets, are widely distributed on tropical and sub-tropical islands where they are eaten by ground-dwelling birds. Combining work on Henderson Island, South Pacific, site of a recent rat eradication project, and UK laboratory experiments, our study first measured brodifacoum concentrations in cockroaches given temporary ad lib access to poison bait pellets, approximately mimicking the aftermath of bait distribution for a rodent eradication. In two separate experiments using different species/exposure times, the mean brodifacoum concentrations among cockroaches immediately after bait exposure was 262±s.e. 131 and 477±168µgkg(-1) wet weight. Values decreased quickly in the following 2 weeks, and then continued to decline at a slower rate over the following 4 weeks in the more prolonged laboratory experiment. A supplementary experiment with woodlice recorded a similar brodifacoum concentration in the animals at the end of the exposure period, 223±66µgkg(-1), and a similar time course for the post-exposure decline. In the context of rails (Rallidae), a group of birds known to be particularly susceptible to primary brodifacoum poisoning, these results suggested that, in terms of acute exposure, individual birds would need to eat a minimum of their own body weight (and more commonly 2-5 times that) of live cockroaches before facing a 50% risk of death. Therefore, we conclude that in eradication scenarios, acute secondary poisoning is of lower concern for these birds than primary poisoning.
在计划消灭啮齿动物时,通常会使用抗凝血毒药溴敌隆,因此必须将对与目标啮齿动物共存的其他“非目标”物种的影响降到最低,而这些物种实际上可能是灭鼠的受益者。这种影响可能来自于非目标物种摄入含有毒物的诱饵丸时的原发性中毒,也可能来自于非目标物种吃了已摄入溴敌隆的猎物时的继发性中毒。蟑螂和鼠妇可能会觅食诱饵丸,它们广泛分布在热带和亚热带岛屿上,这些岛屿上的地栖鸟类会捕食它们。我们的研究结合了南太平洋亨德森岛(Henderson Island)的工作,该岛最近进行了一次灭鼠项目,以及英国的实验室实验,首次测量了蟑螂在临时自由接触毒饵丸时的溴敌隆浓度,这大致模拟了灭鼠后毒饵分布的后果。在两个使用不同物种/暴露时间的单独实验中,蟑螂在接触诱饵后的即刻溴敌隆浓度平均值分别为 262±s.e. 131 和 477±168µgkg(-1)湿重。在接下来的 2 周内,这些值迅速下降,然后在接下来的 4 周内,在更长期的实验室实验中以较慢的速度继续下降。一项补充的鼠妇实验记录了暴露期结束时动物体内类似的溴敌隆浓度,为 223±66µgkg(-1),暴露后下降的时间过程也相似。就红脚鹬(Rallidae)而言,这是一组已知特别容易受到原发性溴敌隆中毒影响的鸟类,这些结果表明,就急性暴露而言,个体鸟类需要吃下自身体重的最小量(通常是 2-5 倍)的活蟑螂,才会面临 50%的死亡风险。因此,我们的结论是,在灭鼠场景中,这些鸟类急性继发性中毒的风险比原发性中毒低。