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Spatio-temporal changes in density and distribution of burrow-nesting seabird colonies after rat eradication

机译:根除大鼠后洞穴巢海鸟菌落密度和分布的时空变化

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The size and distribution of colonies of burrow-nesting petrels is thought to be limited partly by the availability of suitable breeding habitat and partly by predation. Historically, the availability of safe nesting habitat was restricted in New Zealand, due to the introduction of rats by humans. More recently, however, habitat has been restored by rat eradication. Petrel colony growth is mediated by both positive and negative density dependence, although it is unclear if, or how, density dependence will affect patterns in post-eradication colony recovery. Here, using burrow density as a proxy for relative abundance, we tested whether petrel colonies increase in density or area after rat eradication by sampling along a chronosequence of (1) five islands from which rats were eliminated 1 to 26 years ago, (2) two islands that never had rats, and (3) an island with rats still present, while controlling for habitat availability. We also measured a time series of burrow densities in plots on each island to compare temporal changes after rat eradication. Using Bayesian hierarchical modelling, after controlling for nesting habitat, we found that mean burrow density increased with time since rat eradication. Burrows remained clustered (i.e. spatially structured), but became more randomly distributed on islands with more time since eradication. Point density mapping indicated that colony extent increased with time since rat eradication, with colonies filling over 70% of surveyed areas on islands by 25 years after eradication. Increases in burrow density and colony area, but maintenance of clustered distribution, suggest both positive and negative density dependence may operate during colony expansion. Understanding patterns in petrel colony recovery is important, not only due to the indispensable role of petrels as island ecosystem engineers, reflecting the recovery of ecosystem functioning, but also to help guide post-eradication monitoring strategies.
机译:穴居巢海燕的菌落大小和分布被认为部分受限于合适的繁殖栖息地的可用性,另一部分则受到捕食的限制。从历史上看,由于人类引入了老鼠,因此在新西兰,安全筑巢栖息地的可用性受到限制。然而,最近,通过灭鼠恢复了栖息地。尽管尚不清楚密度依赖性是否或如何影响根除后菌落恢复的模式,但海燕菌落的生长是由正负密度依赖性介导的。在这里,我们使用洞穴密度作为相对丰度的替代指标,通过按时间顺序(1)在1至26年前从中淘汰了五个岛的老鼠,按时间顺序测试了海藻集落在密度和面积上是否增加(2)两个从未有过老鼠的岛屿,以及(3)仍然有老鼠的岛屿,同时控制着栖息地的可用性。我们还测量了每个岛上各地块的洞穴密度的时间序列,以比较根除大鼠后的时间变化。使用贝叶斯分层模型,在控制了筑巢栖息地之后,我们发现,自老鼠灭绝以来,平均洞穴密度随时间增加。洞穴保持聚集(即空间结构),但自消灭以来,散布在岛上的时间越来越长。点密度图表明,自从大鼠根除以来,其集落程度随时间而增加,到根除后25年,该集落已占岛上被调查区域的70%以上。洞穴密度和菌落面积增加,但维持簇状分布,表明在菌落扩展期间可能同时存在正负密度依赖性。了解海燕殖民地恢复的模式很重要,这不仅是因为海燕作为岛屿生态系统工程师所起的不可或缺的作用,反映了生态系统功能的恢复,而且还有助于指导根除后的监测策略。

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