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吉林蛟河近熟林树种多样性格局组建机制研究
引用本文:徐卫,程明杰,林天喜,程艳霞. 吉林蛟河近熟林树种多样性格局组建机制研究[J]. 北京林业大学学报, 2014, 36(6): 80-85. DOI: 10.13332/j.cnki.jbfu.2014.06.016
作者姓名:徐卫  程明杰  林天喜  程艳霞
作者单位:北京林业大学森林资源与生态系统过程北京市重点实验室;吉林市林业调查规划院;吉林省蛟河林业实验区管理局
基金项目:国家自然科学基金项目,北京市科技创新基地培育与发展工程专项,北京林业大学大学生创新项目(S201410022009)。
摘    要:植物种在群落多样性格局组建过程中所起的作用一直是生态学重点关注的问题。2010 年在吉林蛟河建立面积为21.12 hm2 的近熟林监测样地,样地中记录到DBH 1 cm 木本植物32 405 株, 共计50 种木本植物。利用单物种-面积关系模型分析了样地内30 种木本植物对局域群落多样性格局的影响,利用完全空间随机化模拟计算植物对局域多样性促进或抑制的显著性程度。研究结果表明:1)由于ISAR 模型没有考虑竞争的非对称性,在相同取样面积下,同一树种的mISAR 值普遍低于ISAR 值。不同树种的mISAR 曲线更加分散、区分度更为明显,且具有明显的尺度依赖性。2)在0 ~50 m 空间尺度上,簇毛槭、黑樱桃、翅卫矛、稠李、大果榆、花楷槭、毛榛和青楷槭为多样性促进种;水榆为中性种;红松、色木槭、胡桃楸在绝大多数空间尺度上表现为抑制种;其余树种绝大多数在小尺度上表现为促进种。3)在中小尺度上,促进种决定了局域群落多样性格局组建; 在较大尺度上,促进种和中性种共同作用于群落多样性格局的组建,并且随机过程的影响相对更强。因此,促进种和抑制种所代表的确定性过程与中性种所代表的随机过程共同作用于森林群落多样性格局构建过程, 并且二者起作用的空间尺度不同。 

关 键 词:生物多样性  种-面积关系  多样性促进种  中性过程

Structuring mechanism of tree species diversity pattern in a near-mature forest in Jiaohe,Jilin Province
XU Wei,CHENG Ming-jie,LIN Tian-xi,CHENG Yan-xia. Structuring mechanism of tree species diversity pattern in a near-mature forest in Jiaohe,Jilin Province[J]. Journal of Beijing Forestry University, 2014, 36(6): 80-85. DOI: 10.13332/j.cnki.jbfu.2014.06.016
Authors:XU Wei  CHENG Ming-jie  LIN Tian-xi  CHENG Yan-xia
Affiliation:1.1 Key Laboratory for Forest Resources & Ecosystem Processes of Beijing, Beijing Forestry University,2.100083, P. R. China;
Abstract:The effect of plant species on the community diversity pattern has long been a key issue in ecology.A 21.12 hm2 near-mature forest plot was established in Jiaohe of Jilin Province. Totally, 32 405 woodyindividuals with diameter at breast height (DBH) 1 cm belonging to 50 woody species were recorded.Individual species-area relationship (ISAR) was used to quantify the effects of 30 woody species on localcommunity diversity pattern. Complete spatial randomness simulation was adopted to calculate thesignificance of facilitation or suppression. The results show that: 1) ISAR value is generally higher thanmISAR value for the same tree species in the same sampling area, because ISAR model ignoresasymmetry of competition. The mISAR curves for different tree species are more dispersed, and havehigher differnentiation degree and obvious scale dependence. 2) At 0 - 50 m scales, Acer barbinerve,Cerasus maximowiczii, Euonymus macropterus, Padus racemosa, Ulmus macrocarpa, Acer ukurunduense,Corylus mandshurica and Acer tegmentosum are diversity accumulators while Sorbus alnifolia is a neutralspecies. Pinus koraiensis, Acer mono and Juglans mandshurica are diversity repellers at most spatialscales. Most of the other tree species act as diversity accumulators at small scales. 3) Diversityaccumulators dominate the community diversity pattern at the small and medium scales. Diversityaccumulators and neutrals jointly affect the structuring of the community diversity pattern at large scales,and the influence of stochastic process is relatively stronger. Therefore, deterministic process representedby accumulators and repellers and stochastic process represented by neutral species collectively determinethe structuring processes of community diversity pattern, and the effects of two processes differ at differentspatial scales. 
Keywords:biodiversity  species-area relationship  diversity accumulators  neutral processes
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