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Position: Home > Articles > Features of gaps of middle mountain moist evergreen broad-leaved forest in Ailao Mountain Chinese Journal of Ecology 2003,22 (3) 13-17

哀牢山中山湿性常绿阔叶林林窗特征研究

作  者:
李贵才;何永涛;韩兴国
单  位:
中国科学院植物研究所数量植被开放实验室;中国科学院地理科学与资源研究所;中国科学院遥感应用研究所遥感信息科学开放实验室
关键词:
林窗;林窗特征;中山湿性常绿阔叶林
摘  要:
本研究以哀牢山中山湿性常绿阔叶林为研究对象 ,分析了该植被群落林窗的大小结构及干扰形成等空间特征。研究表明 ,林窗大小取决于林窗形成方式和形成木的种类、大小。实际林窗面积远小于扩展林窗面积 ,前者的平均面积仅约为后者的 33 2 %。在数量上 ,实际林窗和扩展林窗的面积分布均呈以上小林窗为主的偏态分布。但在总的林窗面积比例上 ,大林窗的所占的面积比更大。实际林窗中 ,10 0~ 2 0 0m2 的林窗所占面积比达 6 6 4 %。扩展林窗中 ,2 0 0~ 30 0m2 和 4 0 0~ 5 0 0m2 大小的面积比分别为 33 1%和 2 0 6 %。由于该地区冬季强劲的风力 ,林窗形成方式以根倒和折干 ,分虽占形成木总数的 35 %和 2 8%。风力是哀牢山中山湿性常绿阔叶林林窗形成的主要外部驱动力。多数林窗由 1~ 3株形成木造成的。林窗形成木的种类绝大多数为变色锥、木果柯和硬壳柯三种群落上层的优势树种。这三个树种约占林窗形成木的 78%。因此 ,对于林窗发生这种中小尺度干扰事件 ,群落上层的成势树种起着决定性的影响作用。其它冠层水平的乔木 (如亚冠层 )的扰动也可以产生林窗 ,但所占比例很小。林窗形成木的径级呈明显的偏正态分布 ,且以 2 1~ 4 0、4 1~ 6 0和 6 1~ 80cm的径级最为普遍 ,分别占总数的 31 6 %、2 0 0 %和
译  名:
Features of gaps of middle mountain moist evergreen broad-leaved forest in Ailao Mountain
作  者:
LI Guicai 1,4 ,HE Yongtao 2,4 ,HAN Xingguo 3 ( 1Laboratory of Remote Sensing Information Science, Institute of Remote Sensing Application, Chinese Academy of Sciences,Beijing 100101, China; 2Institute of Geographical Science and Natural Resource Research, Chinese Academy of Sciences, Beijing 100101, China; 3Laboratory of Quantitative Vegetation, Institute of Botany, Chinese Academy of Sciences, Beijing 100093, China; 4Xishuangbanna Tropical Botanic Garden, Chinese Academy of Sciences, Kunming 650223, China;)
关键词:
gap, gap features, middle mountain moist evergreen broadleaved forest.
摘  要:
The size structure,disturbance character and forming character of canopy gaps were studied in middle mountain mosit evergreen broadleaf ved forest in Ailao Mountain,Yunnan Province,China.The results showed that the gap size depended on the forming modes of gaps, and the sizes and species of gap maker.The areas of actual gaps was enormously less than the one of extended gaps,and the average of the former was only 33\^2% of the latter.The small gaps were main types for the actual and extended gaps.However,the total area of the large gaps was much more than the small gaps.For the actual gaps,the area of the gaps being more than 100~200 m\+2 was about 66 4% of total area. for the extended gaps,the area of the gaps being more than 200~300 m\+2 and 400~500 m\+2 was about 33\^1% and 20\^6% of the total area. Due to the strong wind in winter, the uproot and snapping were the main types of gap makers,and respectively were 35% and 28% of total number of gap makers. The most gaps were formed of 1~3 gap makers which mostly consited of Castanopsis rufescens,Lithocarpus xylocarpus and Lithocarpus hancei. The three species constituted the 78% of the total gap makers.Under the middle or small scale disturbing, the main arboreal dominant species of upper communicate definitively influenced the gap forming.The distrbution of DBH classes of gap makers mostly varied over 21~40,41~60 and 61~80 cm.The amounts of them were about the 31\^6%,20\^0% and 18\^3% of total amount,respectively. The distribution matched perfectly with the distribution of the gap areas.This indicated that the DHB calsses of the gap makers were closely related to the gap areas.

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