Schulze E-D, Wirth C, Mollicone D, Ziegler W
Max-Planck Institute of Biogeochemistry, Box 100164, 07701, Jena, Germany.
Oecologia. 2005 Nov;146(1):77-88. doi: 10.1007/s00442-005-0173-6. Epub 2005 Oct 22.
The dark taiga of Siberia is a boreal vegetation dominated by Picea obovata, Abies sibirica, and Pinus sibirica during the late succession. This paper investigates the population and age structure of 18 stands representing different stages after fire, wind throw, and insect damage. To our knowledge, this is the first time that the forest dynamics of the Siberian dark taiga is described quantitatively in terms of succession, and age after disturbance, stand density, and basal area. The basis for the curve-linear age/diameter relation of trees is being analyzed. (1) After a stand-replacing fire Betula dominates (4,000 trees) for about 70 years. Although tree density of Betula decreases rapidly, basal area (BA) reached >30 m2/ha after 40 years. (2) After fire, Abies, Picea, and Pinus establish at the same time as Betula, but grow slower, continue to gain height and eventually replace Betula. Abies has the highest seedling number (about 1,000 trees/ha) and the highest mortality. Picea establishes with 100-400 trees/ha, it has less mortality, but reached the highest age (>350 years, DBH 51 cm). Picea is the most important indicator for successional age after disturbance. Pinus sibirica is an accompanying species. The widely distributed "mixed boreal forest" is a stage about 120 years after fire reaching a BA of >40 m2/ha. (3) Wind throw and insect damage occur in old conifer stands. Betula does not establish. Abies initially dominates (2,000-6,000 trees/ha), but Picea becomes dominant after 150-200 years since Abies is shorter lived. (4) Without disturbance the forest develops into a pure coniferous canopy (BA 40-50 m2/ha) with a self-regenerating density of 1,000 coniferous canopy trees/ha. There is no collapse of old-growth stands. The dark taiga may serve as an example in which a limited set to tree species may gain dominance under certain disturbance conditions without ever getting monotypic.
西伯利亚的暗针叶林是一种北方植被,在演替后期以新疆云杉、西伯利亚冷杉和西伯利亚松为主。本文研究了18个代表火灾、风倒和虫害后不同阶段林分的种群和年龄结构。据我们所知,这是首次从演替、干扰后的年龄、林分密度和断面积方面对西伯利亚暗针叶林的森林动态进行定量描述。正在分析树木曲线线性年龄/直径关系的基础。(1)在一场取代林分的火灾后,桦树占主导(4000棵树)约70年。尽管桦树的树木密度迅速下降,但40年后断面积(BA)达到>30平方米/公顷。(2)火灾后,冷杉、云杉和松树与桦树同时建立,但生长较慢,持续长高并最终取代桦树。冷杉的幼苗数量最多(约1000棵树/公顷)且死亡率最高。云杉以100 - 400棵树/公顷的数量建立,死亡率较低,但达到最高年龄(>350年,胸径51厘米)。云杉是干扰后演替年龄的最重要指标。西伯利亚松是伴生种。广泛分布的“北方混交林”是火灾后约120年达到断面积>40平方米/公顷的一个阶段。(3)风倒和虫害发生在老龄针叶林分中。桦树无法建立。冷杉最初占主导(2000 - 6000棵树/公顷),但由于冷杉寿命较短,150 - 200年后云杉成为优势种。(4)在没有干扰的情况下,森林发展成纯针叶树冠层(断面积40 - 50平方米/公顷),自我更新密度为1000棵针叶树冠层树/公顷。老龄林分不会崩溃。暗针叶林可以作为一个例子,说明在某些干扰条件下,有限的树种组合可能占据优势而不会形成单一类型。