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DYNAMICS OF SPECIES DIVERSITY IN THE RESTORATION PROCESS OF ARTIFICIAL SPRUCE CONIFER FOREST IN THE EASTERN EDGE OF QINGHAI-TIBET PLATEAU

青藏东缘岷江上游亚高山针叶林人工恢复过程中物种多样性动态


通过对不同林龄(10~70年)的人工云杉(Picea asperata)林及自然恢复的桦木(Betula utilis var. sinensis)林和天然原始冷杉(Abies faxoniana)林的调查研究,采用Margalef 指数、Simpson 指数、McIntosh 指数、Shannon-Wiener 指数、Pielou 的均匀度指数、Hurlbert 均匀度指数等多样性指数及物种数、个体数和盖度分析了群落乔木层、灌木层、草本层及总体的物种多样性,结果发现:1)人工云杉林的物种多样性随着林龄的增加逐渐上升,林冠郁闭前后上升最快,在50~70 年间下降;其中:乔木层物种多样性先上升,郁闭后下降;灌木层物种多样性郁闭前下降,郁闭后骤然上升,后来缓慢下降;草本层物种多样性在早期阶段很高,随着郁闭度的增大而下降,郁闭后又缓慢回升。2)均匀度的变化幅度不大,变化的趋势基本上与物种多样性相反。3)次生桦木林与同林龄的人工云杉林及天然原始林相比,原始冷杉林的物种丰富度、群落总体、乔木层、草本层优势度(Simpson 指数和MacIntosh 指数)和多样性(Shannon-Wiener 指数)最高,灌木层均匀度最低;人工云杉林的物种丰富度、优势度、群落总体、乔木层、草本层多样性最低,但灌木层的均匀度和多样性最高。4)物种多样性的变化与群落盖度特别是乔木层盖度呈负相关,影响人工云杉林物种多样性恢复的主要因素是其乔木层的盖度过大。5)人工云杉林的物种多样性不仅低于同龄的自然恢复的桦木林,远远低于天然原始林,而且经过70 年的发育,灌木层和草本层的盖度很低,水土保持和水源涵养的生态效益很差。迫切需要调整人工云杉林的群落结构,以恢复其生物多样性,增强其生态效益的发挥。建议在人工云杉林郁闭以后,采取适当的人工干扰如间伐等,降低乔木层的盖度,以促进林下灌草层的发育,既可增强水土保持功能,又可加速物种多样性的恢复。

 

Abstract   Species diversity in total, in the arbor layer, the shrub layer, and the herb layer was studied in artificial spruce (Picea asperata) forests at different ages (10-70 years), secondary birch forests and primitive fir (Abies faxoniana) forest. Several diversity indices were selected for use, which were the Margalef index, Simpson index, McIntosh index, Shannon-Wiener index, Pielou’s even index, Hurlbert’s even index, the number of species and individuals, and the canopy coverage. l) The total species diversity of the artificial spruce forests increased with their age at the younger stages, and increased observably in the process of canopy closure, but decreased slightly in the following stages with some fluctuations. In the arbor layer, the trend was the same as the total. In the shrub layer, the species diversity of the artificial spruce forests decreased slightly with age in the younger stages, but increased observably after the closure of‘ canopy, then decreased slowly later. In the herb layer, the species diversity of the artificial spruce forests was very high at the early stages, but decreased with the process of canopy closure, increased slowly after the canopy closure, but then slowly decreased later. 2) The trend of the even indices was contrasted to the species diversity indices, and the range of fluctuation was small. 3) Among the primitive fir forest, the secondary birch forest and the artificial spruce forest of equal age, the number of species, Margalef index, Simpson index, McIntosh index and Shannon-Wiener index in total, in the arbor layer, in the herb layer of the primitive fir forest were the highest, but the even indices were the smallest; in contrast, the species richness, the Simpson index, MacIntosh index and Shannon-Wiener index in total, in the arbor layer, and in the herb layer of the artificial spruce forest were the lowest, but the even indices were the highest. 4) Dynamics of species diversity were closely related to the degree of canopy coverage of the communities. The species diversity declined with increasing canopy coverage. 5) Species diversity of the artificial spruce forest was not only less than in the secondary homochronous birch forest. And far less than that of the natural primitive forest, but was also lower about 70 years after restoration. And the coverage of the shrub layer and the herb layer was very low, which indicated low efficiency of water and soil conservation. It is necessary to adjust the structure of the artificial spruce forests to restore biodiversity and to enhance the ecological effect of these forests.