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Primary succession trajectories on pumice at Mount St. Helens, Washington

机译:华盛顿圣海伦斯山浮石上的主要演替轨迹

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Questions: Does vegetation become less variable over time? Do floristic trajectories converge during succession? Can either allogenic ( external) or autogenic ( internal) factors predict species patterns during succession? Location: Pumice Plain of Mount St. Helens ( 46.23449 N; 122.15929 W, 1230 m a. s. l.), which was sterilized in 1980 by a direct volcanic blast, then buried in pumice. Methods: We monitored a grid of 200 100-m 2 contiguous plots annually ( 1989-2010) and classified the 2010 data into five community types ( CTs). We characterized plots using external ( e. g. distance from relict sites) and internal ( e. g. moisture) factors and clustered plots by position and habitat factors to assess trajectories. We used redundancy analysis ( RDA) to assess relationships between vegetation and these variables over time. Mantel tests, similarity changes and detrended correspondence analysis ( DCA) were used to evaluate successional trends. Results: Five CTs were weakly related to habitats at this scale. Over time, vegetation became more homogeneous and successional trajectories of plots clustered by position and habitat factors became more similar or developed in parallel. The succession rate slowed fitfully as persistent species became dominant, while Lupinus fluctuated. Mantel tests indicated that relationships between species and environment were maximized using only autogenic factors. RDA found that autogenic factors were stronger than allogenic ones, while explained variance did not increase after 1992 and factor correlations to species stabilized by 1996. Conclusions: The strength of links between vegetation and environment were weak at this scale, yet explained variation stabilized early in succession. As substantial vegetative variation persisted and convergence was far from complete due to weak links to habitat factors, habitat variation and stochastic establishment should be considered by vegetationmanagers.
机译:问题:随着时间的推移,植被变化是否变小了?植物轨迹在演替过程中会聚吗?异源(外部)或自源(内部)因素能否预测演替期间的物种格局?位置:圣海伦斯山的浮石平原(46.23449 N; 122.15929 W,1230 m。s.l。),1980年通过直接火山爆炸进行了消毒,然后埋在浮石中。方法:我们每年(1989-2010年)监测一个200 100-m 2连续样地的网格,并将2010年的数据分为五个社区类型(CT)。我们使用外部因素(例如,距遗迹位置的距离)和内部因素(例如,湿度)对地块进行定性,并通过位置和栖息地因素对地块进行聚类以评估轨迹。我们使用冗余分析(RDA)来评估植被和这些变量之间的关系。壁炉架测试,相似性变化和去趋势对应分析(DCA)用于评估继承趋势。结果:在此规模下,五种CT与栖息地之间的关系微弱。随着时间的流逝,植被变得更加均匀,并且按位置和栖息地因素聚类的地块的演替轨迹变得越来越相似或平行发展。随着羽扇豆占主导地位,而羽扇豆波动,演替率适当降低。壁炉架测试表明,仅使用自生因素,物种与环境之间的关系就会最大化。 RDA发现自生因素要强于异源因素,而1992年以后解释的方差并没有增加,到1996年稳定的与物种的因子相关性。结论:在这个规模上植被与环境之间的联系强度较弱,但解释早在2000年之前变异就稳定了。演替。由于与生境因素的联系薄弱,营养状况仍在持续,并且收敛距离还很遥远,因此植被管理者应考虑生境的变化和随机建立。

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