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1.
海岛植被在全球生物多样性研究中起重要作用,研究海岛植被多样性对于理解海陆相互作用下植物群落的多样性维持机制有重要意义.本研究以庙岛群岛的麻栎群落、刺槐群落、黑松群落、荆条群落4种典型植物群落为对象,采用物种多样性指数、功能多样性指数和结构多样性指数,在群落尺度上探讨了海岛典型植物群落物种、功能、结构多样性间的关系及其对环境因子的响应.结果表明: 黑松群落的物种丰富度与Rao指数高于刺槐群落与麻栎群落,而结构多样性却较低;荆条灌丛的物种、结构多样性均低于森林群落,而功能多样性高于部分森林群落.物种丰富度与Rao指数以及树高多样性间呈显著正相关,与功能均匀度呈显著负相关.结构多样性主要由坡度决定且与坡度呈负相关;功能均匀度与坡度呈正相关,而功能异质性、功能离散度和物种多样性则更多地受土壤理化性质的影响,与土壤容重及土壤总碳呈正相关,与土壤含水率呈负相关.总体而言,庙岛群岛的植物群落多样性格局既有与大陆植被相似的特征,但也有其海岛特殊性.  相似文献   

2.
生物多样性对生态系统功能有重要的影响。作为生物多样性研究的重要方面,物种多样性和功能群多样性引起了生态学者的广泛关注。目前,有关松嫩草地的生物多样性一直缺乏全面而系统的研究。本研究通过对松嫩草地42种植物群落(涉及427个物种)的调查,全面探究了松嫩草地草本植物的生物多样性。从整体上看,松嫩草地主要以禾本科、菊科、豆科植物为主。松嫩草地优势种地上生物量在群落中占绝对优势,其地上生物量与群落地上生物量之间呈极显著正相关(R2=0.904)。不同群落之间物种多样性指数差异很大,其中最主要群落——羊草群落物种丰富度指数(2.6)最小。同时,松嫩草地不同功能群多样性指数之间差异明显,C4禾草为优势种的群落功能群多样性指数明显高于C3禾草为优势种的群落。松嫩草地功能群多样性与物种多样性之间呈极显著正相关(P0.01),功能群多样性在一定程度上能够指示松嫩草地生态系统的生物多样性。  相似文献   

3.
库姆塔格沙漠南缘荒漠植物群落多样性分析   总被引:38,自引:0,他引:38       下载免费PDF全文
 根据20个样地的调查资料,应用重要值计算多样性指数、均匀度指数、丰富度指数 、优势度指数,对库姆塔格沙漠南缘荒漠植物群落物种多样性进行分析。结果表明: 1)荒漠植物群落分布随其生境地貌不同而不同,山前戈壁上分布有合头草(Sympegma regelii)群落,冲积河道低地分布有荒漠林胡杨(Populus euphratica)、多枝柽柳(Tamarix ramosissima)、胀果甘草(Glycyrrhiza inflata)群落,戈壁沙漠过渡带为梭梭(Haloxylon ammodendron)群落,低海拔的沙山上分布有沙拐枣(Calligonum mongolicum)群落、膜果麻黄(Ephedra rzewalskii)群落和梭梭群落。2)荒漠植物群落物种多样性水平较低,群落结构简单,物种组成单一。群落Shannon_Wiener物种多样性水平表现为合头草群落最高(1.706),具有草原化荒漠植被类型的成分;梭梭群落、膜果麻黄群落居中(0.875~0.890),荒漠植被类型特征明显;沙拐枣群落、胡杨群落、多枝 柽柳群落、胀果甘草群落较低(0.079~0.495),荒漠林、盐地沙生灌丛及盐化草甸植被均有零星分布。3)荒漠植物群落结构层次中,灌木层占居主导地位,群落灌木层物种多样性水平(0.769~1.451)远远大于草本层(0.193~0.254),且草本层物种多样性受灌木层影响较大。4)荒漠植物群落物种多样性分布格局表现为经向、纬向和海拔梯度的变化,经向、纬向变化为物种多样性水平较高的草原化植物合头草群落(1.706)向物种多样性水平较低的荒漠植物梭梭群落(1.379)和盐化植物多枝柽柳群落(0.376)的过渡,海拔梯度则 呈现低水平的沙拐枣群落(0.819)到高水平的膜果麻黄群落(0.890)向低水平的梭梭群落 (0.645)变化。荒漠植物群落过渡地带一般具有较高的物种多样性和较低的生态优势度。  相似文献   

4.
  生物多样性与生态系统功能之间的关系及其形成的内在机制还存在很多争议。为了揭示植物群落生产力形成的生态学机制, 采用盆栽方法探讨了物种多样性、物种属性以及施肥水平与植物群落生产力之间的关系。研究结果显示: 在不施肥和每盆施5.0 g磷酸二铵的条件下, 随着物种多样性的增加, 地上生物量增加不显著; 在每盆施10.0 g磷酸二铵的条件下, 随着物种多样性的增加, 地上生物量显著增加。相对于中华羊茅(Festuca sinensis)而言, 垂穗披碱草(Elymus nutans)和垂穗鹅观草(Roegneria nutans)对群落生产力的贡献较大, 但在不同施肥水平和播种密度下, 其影响不完全相同。这表明物种多样性对群落生产力的影响随着土壤肥力的变化而变化; 并且植物群落生产力受组成群落的物种属性影响较大, 而物种属性又与特定时间和特定生境下资源的利用方式相联系。在高肥力水平下, 物种多样性之所以对群落生产力具有正效应, 可能是因为高肥力水平增加了可利用的生态位空间, 最终仍体现在物种组合上。因此, 植物群落的生产力与物种多样性之间没有必然的联系, 而与土壤肥力和土壤肥力决定的物种属性有关。  相似文献   

5.
青海省高寒灌丛物种多样性、生物量及其关系   总被引:1,自引:0,他引:1  
物种多样性对生态系统功能的作用是生物多样性研究的核心领域之一,生物量水平是生态系统功能的重要表现形式,而植物群落的生物量则是生态系统生物量的基础,因此研究植物群落物种多样性与生物量的关系,对于阐明植物多样性对生态系统功能的作用具有重要意义。通过对青海省高寒灌丛生物量、灌丛物种多样性特征以及与生物量的关系调查,得到以下结果:(1)被调查灌木植被群落的40个样地中共出现了207种植物(其中灌木植物18种,草本植物189种),隶属于130属,43科,灌木以蔷薇科、杜鹃花科为主,而草本以菊科、龙胆科、毛茛科和莎草科占优势。(2)群落多样性指数偏低,植物群落结构简单,物种组成稀少。小叶金露梅群落的多样性指数最大,金露梅群落、细枝绣线菊群落和鲜卑花群落次之,百里香杜鹃+头花杜鹃群落最低。(3)不同高寒灌丛类型生物量介于1893.03—7585.41 g/m~2之间,平均值为3775.9 g/m2,其中灌木生物量占灌丛总生物量的73.55%,草本为26.45%。(4)总生物量随草本物种多样性和群落物种多样性的增加而减小;草本生物量随其物种多样性的增加而减小,而灌木物种多样性与其生物量并无显著相关性。  相似文献   

6.
beta多样性反映了群落间物种组成的差异,是生物多样性研究的热点之一。本研究通过对云南元江干热河谷41个植物群落样方进行调查,用Jaccard相异系数表征物种beta多样性,用样方之间的最近谱系距离(mean nearest taxon distance,MNTD)及平均谱系距离(mean pairwise distance,MPD)表征谱系beta多样性,采用基于距离矩阵的多元回归和方差分解方法,探讨了该区域干热河谷典型植物群落的物种beta多样性和谱系beta多样性与样方间环境差异(主要是气候)及地理距离之间的关系。结果表明:(1)群落间的地理距离和年平均温度差异对干热河谷植物群落的物种beta多样性和谱系beta多样性有显著影响;(2)地理距离对物种beta多样性和MNTD的影响最大;地理距离和年平均温度差异对MPD的影响均较大;(3)样方间年平均温度与年平均降水量的差异和地理距离能够解释群落间beta多样性及谱系beta多样性11–13%的变异。以上结果表明,生态位分化和扩散限制对该地区植物群落的beta多样性均有显著影响,其中扩散限制的影响可能更大。此外,人类活动等其他因素也很可能对元江干热河谷的群落组成具有非常重要的影响。  相似文献   

7.
农业景观非农生境植物多样性及其影响因素   总被引:1,自引:0,他引:1  
卢训令  梁国付  汤茜  丁圣彦 《生态学报》2018,38(5):1799-1809
农业景观是人类生活所需资料的最主要来源地和生物多样性保护的重要区域之一。黄河中下游地区是我国最重要的农业区之一,在区域农业景观中,非农生境中各群落植物物种多样性组成特征有何差异?在不同尺度上,景观异质性特征与生境特征对植物物种多样性特征有何影响?在黄河中下游典型区域布点,对区内主要非农生境(次生林、次生灌丛、人工林和农田边缘等)中的植物群落物种多样性进行调查。结果显示:(1)次生灌丛中的物种丰富度和多样性显著高于其他生境,而农田边缘也保育有较多的物种;(2)从物种组成来看,景观尺度上样点间物种多样性差异(β_2)是所有生境中物种丰富度的最主要组成部分,而次生灌丛与次生林两类自然生境中小尺度(α和β1)物种丰富度的贡献相对较高。(3)景观异质性特征指标对物种多样性的影响主要体现在样方尺度上(α_(样方)),而β和γ多样性与之的关系并不甚密切。表征生境特征的群落高度和盖度指标能更好的预测物种多样性的特征。研究发现,常用的表征景观异质性的指数在各尺度上对植物群落物种多样性特征的影响也并不显著,局地群落特征的影响更为直接和重要。在探讨景观异质性特征与生物多样性关系时,常用的多样性指数(Shannon多样性指数、均匀度指数和Simpson指数等)并不合适,而拆分后的物种丰富度会更有效。但景观异质性对生物多样性的影响也不容忽视,它的改变会是影响群落物种多样性及其组成结构的重要潜在因素,在更大尺度上景观异质性会通过对景观组成要素特征(生境组成和构型)的影响进而影响到区域植物物种丰富度的变化。  相似文献   

8.
旅游干扰越来越多地对原生植物群落产生了影响, 为了揭示游步道两侧湿地植物群落对旅游干扰响应过程, 进而制定科学的应对策略, 以游步道两侧湿地植物群落为研究对象, 开展植物群落的野外样方调查, 并使用重要值、生物多样性指数等, 分析了大九湖湿地游步道两侧的主要植物群落及其优势种、旅游干扰对游步道两侧典型植物群落生物多样性及结构等影响。结果表明, 游步道两侧植物群落主要有四大类23个植物群落类型, 并包括58个优势植物种。旅游活动干扰导致了游步道两侧局部湿地植物群落结构的改变, 出现了中生植物群落。旅游活动干扰也已经导致游步道边缘植物群落的物种丰富度和多样性升高、Simpson优势度指数和物种相似度下降、生产力显著降低, 但其影响范围集中在游步道两侧10 m以内。同时, 距游步道越近, 相邻梯度植物群落内物种相似度显著降低, 游步道边缘的植物种类组成更趋向于干化。旅游活动干扰也制约了阿齐苔草(Carex argyi)、庐山藨草(Scirpus lushanensis)等成为游步道两侧植物群落的优势物种。此外, 游步道两侧不同类型的植物群落对旅游活动干扰的耐受性不同, 其响应强度由高到低依次为苔草群落、拂子茅—地榆群落、羊茅群落。  相似文献   

9.
宁夏荒漠草原植物群落结构和物种多样性研究   总被引:13,自引:1,他引:12  
采用样方法对宁夏荒漠草原植物群落进行了调查,对群落结构、功能群物种组成和物种多样性以及群落生产力的关系进行探讨。结果表明,群落生产力除受物种多样性的影响外,也受物种本身特征和环境资源的影响。在荒漠草原中功能群盖度与群落初级生产力无显著的相关关系。功能群内物种多样性、物种数和个体数量上呈现一定的互为消长关系。  相似文献   

10.
《植物生态学报》2014,38(5):417
施肥和刈割分别对植物群落物种多样性和生产力有重要的影响。采用不同施肥水平和刈割频度, 研究了施肥和刈割对亚高山草甸植物群落物种多样性与生产力及其关系的影响。结果显示, 5年的施肥和刈割处理对群落地上生物量均有显著影响, 但对物种多样性影响不显著; 物种多样性与生产力之间的关系因施肥和刈割次数的不同而不同, 有负相关、二次函数关系和不相关等几种类型, 多数为不相关。此结果表明施肥和刈割并不总是一致性地影响群落物种多样性与生产力。因此, 不同施肥和刈割处理下的亚高山草甸植物群落生产力与物种多样性之间并没有确定的关系。  相似文献   

11.
Change in diversity of fossil pollen through time is used as a surrogate for biodiversity history. However, there have been few studies to explore the sensitivity of the measured pollen diversity to vegetation changes and the relationship between pollen diversity and plant diversity. This paper presents results of a study to assess the relationship between pollen diversity and relative abundance of pollen from different altitudinal vegetation belts (subandean forest, Andean forest, subparamo and grassparamo) in three records from the tropical Andes in Colombia. The results indicated that plant diversity in the vegetation declined with altitude and pollen diversity is positively correlated to the abundance of pollen from lower altitude vegetation belts and negatively correlated to that from the grassparamo. These results, therefore, suggest that pollen diversity coarsely reflects the diversity of the surrounding vegetation. Using this interpretation, we were able to predict changes in plant diversity over the past 430000 years in the Colombian Andes. Results indicated that under warmer climatic conditions, more species-diverse vegetation of low elevation moved upslope to contribute more pollen diversity to the study sites, and under colder conditions, species-poor grassparamo moved downslope and observed pollen diversity was lower. This study concludes that fossil pollen diversity may provide an important proxy to reconstruct the temporal changes in plant diversity.  相似文献   

12.
中国东北样带草地群落放牧干扰植物多样性的变化   总被引:20,自引:0,他引:20       下载免费PDF全文
放牧干扰是草地群落植物多样性变化的主要影响因素之一。中国东北样带9个草地群落放牧干扰植物多样性变化的研究结果表明:中牧或重牧阶段Shannon指数达最大值,形成中牧(重牧)>重牧(中牧)>轻牧>过牧的规律。群落物种丰富度、均匀度与多样性的相关分析表明,均匀度变化对多样性变化具有更大的贡献率,而丰富度呈下降趋势,即轻牧(中牧)>中牧(轻牧)>重牧>过牧。生活型功能群多样性也表现出明显的变化。中国东北样带草地群落植物多样性的分布格局是:草甸草原>典型草原>典型草原 >荒漠草原>碱化草原,并且群落物种丰富度对多样性有更大贡献率。  相似文献   

13.
陆地植物群落物种多样性的梯度变化特征   总被引:181,自引:14,他引:167  
研究陆地植物落物种多样性随环境因子及群落演替梯度的变化特征是揭示生物多样性与生态因子相互关系的重要方面,根据近期国内外的文献,综述了这方面的研究进展。随纬度的降低,通常物咱多样性随中,随不分梯度的变化,物种多样性的变化有6种趋势;随海拔高的变化,物处多样性有5种模式;随土壤养分梯度的变化,表现出不同的规律;演替过程中物种多样生的变化趋势相似。关于植物群落物种多样性梯度格局的机制有多种假说,但仍需进  相似文献   

14.
中国东北样带草地群落放牧干扰植物多样的变化   总被引:33,自引:0,他引:33  
放牧干扰是草地群落植物多样性变化的主要影响因素之一。中国东北样带9个草地群落放牧干扰植物多样性性变化的研究结果表明:中牧或重牧阶段Shannon指数达最大值。形成中牧(重牧)>重牧(中牧)>轻牧>过牧的规律。群落物种丰富度、均匀度与多样性的相关分析表明,均匀度变化对多样性变化具有更大的贡献率。而丰富度呈下降趋势,即轻牧(中牧)>中牧(轻牧)>重牧>过牧。生活型功能群多样性也表现出明显的变化。中国东北样带草地群落植物多样性的分布格局是:草甸草原>典型草原>典型草原>荒漠草原>碱化草甸,并且群落物种丰富度对多样性有更大贡献率。  相似文献   

15.
As revealed in this study, S. sonnei population is represented by two clusters with respect to the sensitivity to different antibiotics. A higher degree of diversity was observed with respect to the action of streptomycin, kefzol, ampicillin, chloramphenicol and kanamycin in comparison with the action of gentamicin, nevigramon, rafampicin, tetracycline and polymyxin. The level of diversity of S. sonnei with respect to the sensitivity to antibiotics under study underwent essential changes during the calendar year. The distributions obtained study quite closely corresponded to changes in Sonne dysentery morbidity observed within the year period: the first cluster corresponded to the period of morbidity between the seasons and the second one, to the seasonal period of morbidity. The minimal coefficient of diversity fell on May while the maximum--on September. The minimal level of S. sonnei diversity, as a rule, corresponds to the minimum biosystems stability.  相似文献   

16.
Elevation is involved in determining plant diversity in montane ecosystems. This study examined whether the distribution of plants in the Yatsugatake Mountains, central Japan, substantiated hypotheses associated with an elevational diversity gradient. Species richness of trees, shrubs, herbs, ferns, and bryophytes was investigated in study plots established at 200‐m elevational intervals from 1,800 to 2,800 m. The changes in plant diversity (alpha and beta diversities, plant functional types, and elevational ranges) with elevation were analyzed in relation to climatic factors and elevational diversity gradient hypotheses, that is, mass effect, mid‐domain effect, and Rapoport''s elevational rule. In addition, the elevational patterns of dominance of plant functional types were also analyzed. A comparison of alpha and beta diversities revealed that different plant groups responded variably to elevation; the alpha diversity of trees and ferns decreased, that of herbs increased, whereas the alpha diversity of shrubs and bryophytes showed a U‐shaped relationship and a hump‐shaped pattern. The beta diversity of shrubs, herbs, and bryophytes increased above the subalpine–alpine ecotone. In accordance with these changes, the dominance of evergreen shrubs and graminoids increased above this ecotone, whereas that of evergreen trees and liverworts decreased. None of the plant groups showed a wide elevational range at higher elevations. These elevational patterns of plant groups were explained by climatic factors, and not by elevational diversity gradient hypotheses. Of note, the changes in the dominance of plant groups with elevation can be attributed to plant–plant interactions via competition for light and the changes in physical habitat. These interactions could alter the elevational diversity gradient shaped by climatic factors.  相似文献   

17.
Although it is generally recognized that global biodiversity is declining, few studies have examined long‐term changes in multiple biodiversity dimensions simultaneously. In this study, we quantified and compared temporal changes in the abundance, taxonomic diversity, functional diversity, and phylogenetic diversity of bird assemblages, using roadside monitoring data of the North American Breeding Bird Survey from 1971 to 2010. We calculated 12 abundance and diversity metrics based on 5‐year average abundances of 519 species for each of 768 monitoring routes. We did this for all bird species together as well as for four subgroups based on breeding habitat affinity (grassland, woodland, wetland, and shrubland breeders). The majority of the biodiversity metrics increased or remained constant over the study period, whereas the overall abundance of birds showed a pronounced decrease, primarily driven by declines of the most abundant species. These results highlight how stable or even increasing metrics of taxonomic, functional, or phylogenetic diversity may occur in parallel with substantial losses of individuals. We further found that patterns of change differed among the species subgroups, with both abundance and diversity increasing for woodland birds and decreasing for grassland breeders. The contrasting changes between abundance and diversity and among the breeding habitat groups underscore the relevance of a multifaceted approach to measuring biodiversity change. Our findings further stress the importance of monitoring the overall abundance of individuals in addition to metrics of taxonomic, functional, or phylogenetic diversity, thus confirming the importance of population abundance as an essential biodiversity variable.  相似文献   

18.
The study of ecological communities through time can reveal fundamental ecological processes and is key to understanding how natural and human pressures will affect biodiversity. Most studies of ecological communities through time consider only one or a few summary measures (e.g. species richness, total abundance), which might neglect important aspects of community structure or function. We studied temporal variation in several measures of species diversity, size diversity, and species composition in an intensively sampled bird community to determine whether different biodiversity measures change synchronously. We used a novel function regression model, which supports the study of diversity measures that are distributions (e.g. species abundance distributions) alongside measures that are scalar values (e.g. species richness). Most diversity measures changed predictably within years, but inter‐annual changes in size diversity and species composition were not reflected in species diversity. Within and among years, there was considerable variation in distributional measures that was not captured in scalar measures. Predictable variation within years probably was related to seasonal variation in weather patterns or food availability, but variation in size diversity among years probably resulted from stochastic changes in species composition. These results suggest that species and size diversity may be decoupled, and that inferences on scalar diversity measures might not reflect fundamental changes to community structure or function. Our method supports the inclusion of size‐based measures and distributional measures in ecological analyses, and broader uptake of our approach is likely to provide new insight into the processes structuring ecological communities, and inform the links between structure and function in ecological communities.  相似文献   

19.
This study evaluates putative changes of genetic diversity and relationships of barley in the Nordic and Baltic countries that might have taken place during the last century as a result of commercial breeding. Four ISSR primers were used to analyse 227 accessions, yielding a total of 47 polymorphic loci. Shannon-Weaver diversity values for each locus ranged from 0.012 to 0.693. Overall, there were no significant changes of genetic diversity observed over time. A significant decrease of diversity was, however, observed in material from the southern parts of the Nordic and Baltic countries. In material from the northern parts no decrease of diversity was observed. The genetic diversity of six-rowed barley bred in the middle of the 20th century was low, but there was no significant difference between modern accessions and landraces or old cultivars. The magnitude in changes of genetic diversity differed also in material from different countries of origin. A cluster analysis clearly separated the material into two groups. The first cluster included 86.5% of all six-rowed accessions, whereas the second cluster contained 97.4% of all two-rowed accessions.  相似文献   

20.
Studies on the effects of plant diversity on insect herbivory have produced conflicting results. Plant diversity has been reported to cause positive and negative responses of herbivores. Explanations for these conflicting responses include not only various population-level processes but also changes in plant quality that lead to changes in herbivore performance. In a tree diversity experiment, we investigated the effects of tree diversity on insect herbivory on oak in general and whether the effects of tree diversity on herbivore damage are reflected by the performance (leaf consumption, growth) of the generalist herbivore Lymantria dispar. Our study showed that the feeding damage caused by naturally occurring herbivores on oak trees decreased with increasing diversity of tree stands. The performance of L. dispar on oak leaves was not affected by tree diversity, neither in field nor laboratory experiments. Our results can be explained by the various processes behind the hypothesis of associational resistance.  相似文献   

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