Research Corporation of the University of Guam, Mangilao, Guam, USA.
Swiss Federal Institute for Forest, Snow and Landscape Research WSL, Birmensdorf, Switzerland.
Ecol Appl. 2022 Dec;32(8):e2716. doi: 10.1002/eap.2716. Epub 2022 Sep 30.
The brown treesnake (BTS) (Boiga irregularis) invasion on Guåhan (in English, Guam) led to the extirpation of nearly all native forest birds. In recent years, methods have been developed to reduce BTS abundance on a landscape scale. To help assess the prospects for the successful reintroduction of native birds to Guåhan following BTS suppression, we modeled bird population persistence based on their life history characteristics and relative sensitivity to BTS predation. We constructed individual-based models and simulated BTS predation in hypothetical founding populations for each of seven candidate bird species. We represented BTS predation risk in two steps: risk of being encountered and risk of mortality if encountered. We link encounter risk from the bird's perspective to snake contact rates at camera traps with live animal lures, the most direct practical means of estimating BTS predation risk. Our simulations support the well-documented fact that Guåhan's birds cannot persist with an uncontrolled population of BTS but do indicate that bird persistence in Guåhan's forests is possible with suppression short of total eradication. We estimate threshold BTS contact rates would need to be below 0.0002-0.0006 snake contacts per bird per night for these birds to persist on the landscape, which translates to an annual encounter probability of 0.07-0.20. We simulated the effects of snake-proof nest boxes for Sihek (Todiramphus cinnamominus) and Såli (Aplonis opaca), but the benefits were small relative to the overall variation in contact rate thresholds among species. This variation among focal bird species in sustainable predation levels can be used to prioritize species for reintroduction in a BTS-suppressed landscape, but variation among these species is narrow relative to the required reduction from current BTS levels, which may be four orders of magnitude higher (>0.18). Our modeling indicates that the required predation thresholds may need to be lower than have yet been demonstrated with current BTS management. Our predation threshold metric provides an important management tool to help estimate target BTS suppression levels that can be used to determine when bird reintroduction campaigns might begin and serves as a model for other systems to match predator control with reintroduction efforts.
棕色树蛇(Boiga irregularis)入侵关岛导致几乎所有本地森林鸟类灭绝。近年来,已经开发出了在景观尺度上减少棕色树蛇数量的方法。为了帮助评估在棕色树蛇抑制后成功将本地鸟类重新引入关岛的前景,我们根据其生活史特征和对棕色树蛇捕食的相对敏感性,对鸟类种群的持久性进行了建模。我们构建了基于个体的模型,并对七种候选鸟类的每个物种的假设创始种群进行了模拟棕色树蛇捕食。我们分两步表示棕色树蛇捕食风险:遇到的风险和遇到时死亡的风险。我们将从鸟类角度来看的遭遇风险与带有活体诱饵的相机陷阱中的蛇接触率联系起来,这是最直接的估计棕色树蛇捕食风险的实用方法。我们的模拟结果支持了一个有据可查的事实,即在没有棕色树蛇不受控制的情况下,关岛的鸟类无法生存,但确实表明,如果不彻底消灭棕色树蛇,关岛森林中的鸟类就有可能生存下去。我们估计,这些鸟类要在景观中生存,棕色树蛇的接触率必须低于每只鸟每夜 0.0002-0.0006 次,这相当于每年的遭遇概率为 0.07-0.20。我们模拟了 Sihek(Todiramphus cinnamominus)和 Såli(Aplonis opaca)的防蛇巢箱的效果,但与物种之间接触率阈值的整体差异相比,这些好处很小。这些焦点鸟类物种在可持续捕食水平上的差异可以用于优先考虑在棕色树蛇抑制的景观中重新引入的物种,但与目前棕色树蛇水平相比,这些物种之间的差异很小,目前棕色树蛇水平可能高出四个数量级以上(>0.18)。我们的模型表明,所需的捕食阈值可能需要低于当前棕色树蛇管理所证明的水平。我们的捕食阈值指标提供了一个重要的管理工具,可以帮助估计目标棕色树蛇抑制水平,从而可以用来确定何时可以开始鸟类重新引入活动,并为其他系统提供模型,将捕食者控制与重新引入工作相匹配。