Conservation Science Research Group, School of Environmental and Life Sciences, Biology Building, University of Newcastle, University Drive, Callaghan, NSW, 2308, Australia; FAUNA Research Alliance, PO Box 5092, Kahibah, NSW, 2290, Australia.
Conservation Science Research Group, School of Environmental and Life Sciences, Biology Building, University of Newcastle, University Drive, Callaghan, NSW, 2308, Australia.
J Environ Manage. 2021 Aug 1;291:112638. doi: 10.1016/j.jenvman.2021.112638. Epub 2021 May 4.
Amphibians have declined due to multiple impacts including invasive fish and the disease chytridiomycosis caused by the chytrid fungus Batrachochytrium dendrobatidis (Bd). Wetland restoration can be used to increase amphibian populations. However the design of created wetlands must account for threats such as Bd and introduced fish. There have been no attempts on a landscape level to manage these threats with habitat design. Here we monitored the green and golden bell frog (Litoria aurea) in 2.6 ha of constructed wetlands designed to enhance breeding and increase survival through passive mitigation of Bd and exotic fish. We compared the fecundity, adult population sizes, introduced fish occupancy, Bd prevalence and survival rates of frogs in created wetlands (CW) to three control sites to determine if and why the habitat design was successful. Monitoring involved weekly capture-recapture during the austral spring and summer for three L. aurea breeding seasons. We hypothesised that (1) if the CWs were successful in passively limiting fish colonisation, a larger number of breeding events would be detected compared to control sites which are known to be widely colonised by introduced fish. (2) If the wetlands were successful in passively mitigating Bd, then we would observe an equal or greater survival rate and equal to or lower Bd prevalence compared to control wetlands. We observed a 3.3-fold increase in adult population size in CW from season 1 to 2, and the population increased further in season 3.We found strong support for hypothesis (1) and weak support for (2). Based on these results, we conclude that this design was beneficial shortly after their formation primarily due to fish exclusion, but further study is required to determine if these benefits extend long-term. Future amphibian restoration studies are needed to improve the design of wetlands to enhance suppression of Bd.
两栖动物由于多种因素而减少,包括入侵鱼类和由真菌蛙壶菌(Batrachochytrium dendrobatidis,Bd)引起的疾病。湿地恢复可以用于增加两栖动物的数量。然而,人工湿地的设计必须考虑到 Bd 和引入鱼类等威胁。在景观层面上,还没有人试图通过栖息地设计来管理这些威胁。在这里,我们监测了建造的 2.6 公顷湿地中的绿金蛙(Litoria aurea),这些湿地旨在通过 Bd 和外来鱼类的被动缓解来增强繁殖并提高存活率。我们将建造湿地(CW)中的青蛙的繁殖力、成年种群大小、引入鱼类的占有率、Bd 的流行率和存活率与三个对照点进行了比较,以确定栖息地设计是否成功以及为什么成功。监测涉及在澳大利亚春季和夏季的三个繁殖季节中每周进行一次捕获-再捕获。我们假设:(1) 如果 CW 成功地被动限制鱼类的定居,那么与已知广泛定居有引入鱼类的对照点相比,将会检测到更多的繁殖事件。(2) 如果湿地成功地被动减轻了 Bd 的影响,那么我们将观察到与对照湿地相比,存活率相等或更高,Bd 的流行率相等或更低。我们观察到 CW 中的成年种群大小从第 1 季到第 2 季增加了 3.3 倍,第 3 季的种群进一步增加。我们强烈支持假设 (1),而对假设 (2) 的支持较弱。根据这些结果,我们得出结论,这种设计在其形成后不久就具有有益效果,主要是由于鱼类的排除,但需要进一步的研究来确定这些益处是否会长期存在。需要进一步的两栖动物恢复研究来改进湿地设计,以增强对 Bd 的抑制作用。