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首页> 外文期刊>Ecological research >A vegetation change during a 20-year period following two continuous disturbances (mass-dieback of pine trees and typhoon damage) in the Pinus-Schima secondary forest on Chichijima in the Ogasawara (Bonin)
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A vegetation change during a 20-year period following two continuous disturbances (mass-dieback of pine trees and typhoon damage) in the Pinus-Schima secondary forest on Chichijima in the Ogasawara (Bonin)

机译:在小gas原(Bonin)千岛的松树-希马次生林中两次连续的扰动(松树的大规模毁灭和台风破坏)之后的20年中,植被发生了变化。

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摘要

Three permanent plots (P1, P2, and P3) were established in the Pinus luchuensis-Schima mertensiana forest on Chichijima in the Ogasawara Islands. The complete process of the mass-dieback of the pine trees in the early 1980s and the consequences of the typhoon damage in 1983 were surveyed for 20 years (1980-1999) together with the vegetation recovery following these disturbances. The stem height and the growth condition of all the seedlings and saplings (P1: 1,632, P2: 1,681, and P3: 931) were recorded, and the relative light intensity and the weight of the A_0 layer were measured each year. Dead pine trees fell down and rotted gradually. In P1 and P2, the 1983 typhoon inflicted extensive damage to the canopy; the gap area ratio in the canopy was 60.1% and 58.1%, respectively. Trema orientalis seedlings emerged from buried seed concurrently in 1984, but they almost all died within a few years in P2. Many seedlings of S. mertensiana germinated in 1985 and 1986 in P1 and P2, and Psidium cattleianum (an introduced species) followed, especially in P2. Psidium attained a dominant position in the canopy of P2 as a result of the disturbances. In contrast, the structure and composition of the forest in P3, which consisted of emergent trees of Casuarina equisetifolia, did not change to any large extent. All of the individuals found in the plots, with the exception of the parent trees, were classified as advanced saplings (existing from 1980) and new seedlings (germinated during the survey period), and survival rates at 1, 10, and 20 years and growth following the disturbances were compared between them. By 1999, the advanced saplings, but not the new seedlings, overwhelmingly occupied the vacant spaces created in the canopy. Some seedlings became new advanced saplings following the disturbances. Based on these results, a two-step regeneration model that is related to the disturbances is proposed.
机译:在小gas原群岛千岛岛的luchuensis-Schima mertensiana森林中建立了三个永久性地块(P1,P2和P3)。调查了20年代(1980-1999年)的松树大规模灭绝的整个过程以及1983年台风破坏的后果以及这些干扰后的植被恢复。记录所有幼苗和幼树的茎高和生长状况(P1:1,632,P2:1,681和P3:931),并每年测量相对光强度和A_0层的重量。枯死的松树倒下并逐渐腐烂。在P1和P2中,1983年的台风对树冠造成了广泛的破坏。冠层的间隙面积比分别为60.1%和58.1%。 1984年,Trem Orientalis幼苗从埋藏的种子中同时出现,但是在P2中,它们几乎都在几年之内死亡。 1985年和1986年,S。mertensiana的许多幼苗在P1和P2中发芽,随后出现了牛si(Psidium cowianum)(一种引进种),尤其是P2。由于干扰,在P2的冠层中,Ps占据了主导地位。相比之下,由木麻黄(Casuarina equisetifolia)的萌芽树木组成的P3森林的结构和组成在很大程度上没有变化。在地块中发现的所有个体,除亲本树外,均被分类为高级幼树苗(1980年存在)和新苗(在调查期内发芽),存活率分别为1年,10年和20年,以及比较了干扰后的增长。到1999年,先进的树苗(而不是新的树苗)绝大多数占据了树冠中的空置空间。受干扰后,一些幼苗成为新的高级幼树。基于这些结果,提出了与干扰有关的两步再生模型。

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