首页> 外文期刊>Journal of Vegetation Science >Changes in fire intensity have carry-over effects on plant responses after the next fire in southern California chaparral.
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Changes in fire intensity have carry-over effects on plant responses after the next fire in southern California chaparral.

机译:在加利福尼亚州南部丛林的下一场大火之后,火势的变化会对植物的反应产生影响。

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Question: Do variations in fire intensity within a stand determine changes in fire intensity and plant demographics in a subsequent fire? Location: San Diego (CA, USA); chaparral dominated by Adenostoma fasciculatum (resprouter) and Ceanothus greggii (seeder). Methods: In 2003, a wildfire burned a young (16-yr-old) stand containing a set of experimental plots burned in 1987 with various levels of fire intensity. In 2004, all the 1987 plots were sampled for Adenostoma survival and the recruitment of both species. Similar measures were carried out in the adjacent old (75-yr) stand. Fire intensity in 2003 was estimated by a surrogate fire severity measure [minimum diameter of burned branches (branch diameter)]. Results: In the young stand, branch diameter in 2003 was similar to the control plots in 1987, but lower than in the old stand. Fire intensity in 1987 did not significantly affect branch diameter in 2003. Survival of Adenostoma in the young stand was very low, much lower than after the 1987 burn and that in the old stand. Fire intensity in 1987 did not affect Adenostoma survival. Recruitment in Adenostoma increased, and in Ceanothus decreased, with increased fire intensity in 1987. Conclusions: We demonstrate that there is a carry-over effect of fire intensity across a whole fire cycle on plant recruitment of the two dominant species. The 2003 fire partially reversed the relative effects on recruitment caused by elevated fire intensity in 1987. Arguably, this effect was driven by the contrasted relationships of the two species to fire intensity. Adenostoma survival in the young stand was much lower in 2003 than in 1987, despite similar branch diameter, and was also lower than in the old stand, despite higher branch diameter in this case. The causes of such mortality are unknown.Digital Object Identifier http://dx.doi.org/10.1111/j.1654-1103.2012.01466.x
机译:问题:展位内火势的变化是否会决定随后火势的火势变化和工厂人口统计数据?地点:圣地亚哥(美国加利福尼亚州);礼拜室以淡腺腺瘤(reprouter)和灰ean鱼(Ceanothus greggii)(播种者)为主。方法:2003年,一场野火烧毁了一个年轻的(16岁)林分,其中包含一组在1987年燃烧的实验性地块,其火力水平各不相同。 2004年,对1987年的所有地块进行了腺瘤生存和这两个物种的募集的采样。在邻近的旧(75年)看台上也采取了类似的措施。 2003年的火灾强度是通过替代火灾严重程度[燃烧的树枝的最小直径(分支直径)]估算的。结果:在幼林中,2003年的树枝直径与1987年的对照样地相似,但比旧林中的小。 1987年的火势对2003年的分支直径没有显着影响。年轻林分中腺瘤的存活率非常低,远低于1987年烧伤后和老林分中的。 1987年的火势并未影响腺瘤的生存。 1987年,随着火势的增加,腺瘤的招募增加了,而在Ceanothus的招募减少了。结论:我们证明,火势在整个火周期中对两种优势种的植物招募具有结转效应。 2003年的大火在一定程度上扭转了1987年火势增强对招募的相对影响。可以说,这种影响是由两种物种与火势的对比关系驱动的。尽管分支直径相似,但幼林中的腺瘤生存率在2003年比1987年要低得多,尽管在这种情况下,尽管其分支直径较大,但其仍比旧林中的低。这种死亡率的原因尚不清楚。数字对象标识符http://dx.doi.org/10.1111/j.1654-1103.2012.01466.x

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