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克隆重现濒危植物物种:以阿尔卑斯山前河流中的德国假柽柳为例。

Clonal re-introduction of endangered plant species: the case of German False Tamarisk in pre-alpine rivers.

机构信息

Restoration Ecology, Center of Life and Food Sciences Weihenstephan, Technische Universität München, Freising, Germany.

出版信息

Environ Manage. 2012 Aug;50(2):217-25. doi: 10.1007/s00267-012-9880-z. Epub 2012 May 31.

DOI:10.1007/s00267-012-9880-z
PMID:22648658
Abstract

The scope of re-introduction as a measure for plant species protection is increasing, but as long as no standardized methods are available, species-specific assessments are necessary to determine whether seeds, adult plants or plant fragments should be used. The endangered German False Tamarisk (Myricaria germanica), which occurs on gravel bars along pre-alpine rivers, is difficult to grow from seeds. Thus, propagation of stem cuttings was investigated as an alternative method. Experiments were conducted in a greenhouse and a field site with three treatments: cutting length 5 or 10 cm, vertical burial 5 or 10 cm, and water level low or high. Plants grown in the greenhouse were transplanted to the River Isar to test establishment of rooted cuttings on gravel bars. The cuttings in the greenhouse showed high survival (34-96 %). Survival and biomass production were greatest for 10-cm cuttings buried at 10-cm depth, while only one of the 5-cm cuttings survived at this depth, and no significant effect of variation in water level was observed. None of the cuttings transplanted to field sites survived, most likely because of drought stress and competition. We conclude that for re-introduction of Myricaria germanica rooted cuttings can be easily produced in large quantities, while transplantation to near-natural environments has to be improved to reduce mortality.

摘要

重新引入作为植物物种保护措施的范围正在扩大,但只要没有标准化的方法,就需要进行特定于物种的评估,以确定应该使用种子、成年植物还是植物碎片。濒危的德国假柽柳(Myricaria germanica)生长在阿尔卑斯山前河流的砾石滩上,很难从种子中生长。因此,研究了茎段扦插作为替代方法。在温室和野外进行了实验,有三种处理:切割长度为 5 或 10 厘米,垂直掩埋 5 或 10 厘米,水位低或高。在温室中生长的植物被移植到伊萨尔河,以测试生根插条在砾石滩上的建立情况。温室中的插条成活率很高(34-96%)。10 厘米长、埋深 10 厘米的插条的成活率和生物量最大,而在这个深度只有一个 5 厘米长的插条存活,水位变化没有显著影响。没有一个插条在野外试验点存活,最可能的原因是干旱胁迫和竞争。我们得出结论,对于 Myricaria germanica 的重新引入,可以很容易地大量生产生根插条,而移植到近自然环境中必须加以改进,以降低死亡率。

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本文引用的文献

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