生态交错带与生物多样性

自从生态交错带提出以来,许多生态学家对它与生物多样性之间的关系进行了研究,大量的事实显示出生态交错带富于生物多样性,但一些数据也相当模糊。生态交错带的管理和生物多样性保护是一项有意义而紧迫的工作     

生态交错带宽度判定及其影响因子研究进展

生态交错带是相邻生态系统之间的过渡带,是生态系统结构和功能在时、空尺度上变化较快的区域,也是生物多样性丰富区、全球变化敏感区.生态交错带位置和宽度的判定是定量研究交错带生态过程的基础,对生物多样性保护、片断化森林生态系统的管理与恢复以及自然保护区的功能分区都具有重要意义.由于生态交错带本身的复杂性,在相当程度上依赖于尺度水平,并受到各种自然和人为因素的影响,以致于目前还缺乏公认的原理和方法定量研究生态交错带,对其位置、宽度判定和动态变化研究一直处于不断的探索中.在分析大量相关研究资料的基础上,文章对生态交错带宽度判定方法以及影响因子进行论述,并对生态交错带宽度判定的研究前景进行展望.     

城乡交错带的生态控制论分析──天津实例研究

本文应用人类生态学原理和复合生态系统理论,选择城市系统和乡村系统的交错过渡地域－城乡交错带为研究对象,对城乡交错带的概念内涵作了生态学分析。借助生态控制论原理和灵敏度模型方法,以天津城乡交错带为实例,探讨了一个具有典型社会、经济、自然复合生态边缘效应特征的人类生态系统的重庆控制论行为与机制。     

生态空间理论与景观异质性

概述生态空间理论的若干主要方面：尺度、空间格局、景观异质性、镶嵌与生态交错带以及干扰与景观动态等。生态空间理论是景观评价,管理和生态规划的重要基础,对于区域可持续发展和生物多样性保护等方面的研究都具有重要的指导意义。     

景观生态网络研究进展

作为生态学重要的概念与方法,生态网络是景观生态学研究的热点问题,也是耦合景观结构、生态过程和功能的重要途径。景观生态网络对于保护生物多样性、维持生态平衡、增加景观连接度具有重要意义。从景观生态网络的相关理论、研究进展、研究方法模型等进行分析,并对其应用前景进行展望,主要介绍了传统景观格局分析、网络分析、模型模拟等方法的适用性与特点,并分析了景观生态网络在城市景观格局优化、自然保护区规划、生物多样性保护、土地规划等领域的应用,最后提出了研究的主要问题。     

长白山森林/沼泽生态交错带群落和环境梯度分析

揭示了森林沼泽过渡带群落的结构、生产力、植物多样性等群落梯度和交错带环境梯度的相关规律,并结合交错区环境梯度分析这些群落特征形成机制,为维持、保护与经营管理这一交错带生物资源提供了理论依据.将长白山地区森林和高、中、低位沼泽所形成的三大类型过渡带作为研究对象,采用样带网格的调查方法,并应用系统软件分析方法建立了经验回归模型,研究了森林/沼泽生态交错带群落的种类组成、群落建群种径级结构与年龄结构、植物多样性、群落生产力及其随生态交错带环境梯度变化趋势.结果表明,森林/沼泽生态交错带群落结构特征、植物多样性、群落生产力均随着交错带环境梯度的变化而呈现有规律的分布格局.沿着沼泽至森林方向的交错区环境梯度,群落建群种发生更替现象;群落种类数目呈现指数递增趋势;群落的径级结构呈现双曲线分布规律性;年龄结构一般呈三次式分布规律;植物多样性呈二次式递增分布趋势;群落生物量均呈现三次式函数曲线递增趋势,表现出群落梯度和环境梯度的高度相关性.     

群落构建的中性理论和生态位理论

物种共存和生物多样性维持一直是生态学研究的中心论题。基于物种生态位分化的群落构建理论已经发展了近一个世纪, 但我们对群落构建和生物多样性维持的机理仍然不清楚。近年来, 群落中性理论以其简约性和预测能力成为群落生态学研究的焦点, 但由于其“物种在生态功能上等价”的假设与大量研究结果相悖, 同时对自然群落结构的准确预测也只限于少数的生态系统, 因而饱受质疑。如今, 越来越多的生态学家认为群落构建的生态位理论与中性理论之争的最终归宿应该是二者的整合。 在本文中, 我们在简要回顾生态位理论和群落中性理论发展的基础上, 分析二者之间的主要分歧和互补性, 试图梳理二者整合的途径。我们认为, 尽管中性理论的发展极大地丰富了群落构建理论, 但二者的整合尚处于初级阶段; 群落构建零模型假说、中性—生态位连续体假说、随机生态位假说等都不失为有价值的尝试, 今后需要在其他类型的生态系统中进行实验验证, 以更好地理解确定性过程和随机过程在决定群落构建和生物多样性维持中的作用。     

甘肃祁连山脉雪豹及其同域分布大型食肉动物时间生态位关系

<正>群落内多物种如何共存是群落生态学和生物多样性研究的核心内容之一。经典物种共存理论强调物种之间的生态位分化,侧重于物种对环境的需求,Hutchinson (1957)提出超体积生态位概念,认为物种适合度是由多个因素共同决定,即物种只有在满足其生态位需求的多维空间,     

生物多样性理论最新进展

生物多样性是生态系统复杂性的重要特征, 理解多样性的形成和维持机制一直是理论生态学研究的核心议题。本文从三方面概述了生物多样性理论的最新进展。一是物种共存和群落构建, 总结了现代共存理论和基于过程的群落构建理论的新进展。二是物种相互作用, 综述了利用经验数据推断物种相互作用关系和强度的最新方法。三是生态-进化动态, 介绍了生态-进化模型的一般框架及其在生物多样性研究中的应用。最后对生物多样性理论的发展趋势做了展望, 特别是多尺度整合理论和全球变化下的预测理论。     

长白山森林／沼泽生态交错带群落和环境梯度分析

揭示了森林－沼泽过渡带群落的结构、生产力、植物多样性等群落梯度和交错环境梯度的相关规律,并结合交错区环境梯度分析这些群落特征形成机制,为维持、保护与经营管理这一交错带生物资源提供了理论依据。将长白山地区森林和高、中、低位沼泽所形成的三大类型过渡带研究对象,采用样带网格的调查方法,并应用系统软件分析方法建立了经验回归模型,研究了森林／沼泽生态交错带群落的种类组成、群落建群种径级结构与年龄结构、植物多样性、群落生产力及其随生态交错带环境梯度变化趋势。结果表明,森林／沼泽生态交错带群落结构特征、植物多样性、群落生产力均随着交错带环境梯度的变化而呈现有规律的分布格局,沿着沼泽至森林方向的交错区环境梯度,群落建种种发生更替现象;群落种类数目呈现指数递增趋势;群落的径级结构呈现双曲线分布规律性;年龄结构一般呈三次式分布规律;揿样性呈二次式梯增分布趋势;群落生物量均呈现三次函数曲线递增趋势,表现出群落梯度和环境梯度的高度相关性。     

生态交错带的定量判定

生态过渡性是梯度环境的特征之一,过渡带的显著性是地理学和地植物学中长期争论的重要问题,生态交错带位置和宽度的判定是定量研究交错带生态学过程的基础。样带法是采集非连续梯度数据和研究交错带的结构,功能和格局梯度变化的有效方法。生态交错带变化最为显著的特征是植被的变化,包括植物种类组成和植被结构的变化,植被生态学群落分析中的相异系数,β多样性,梯度分析和分类排序技术等已被证明是成熟可靠的方法。介绍两种交错带定量判定的有效方法。游动分割窗技术是通过滑动求取样带上样点间相异系数,通过相异系数变化曲线判定交错带的位置和宽度。分割窗技术提供了敏感地定位非连续梯度的客观且有效的方法,它不仅可用于环境梯度上的等距离样点取样,而且可用于非等距离梯度带多元变量的分析。植被的特征是对生态环境连续体的综合反应,植被在环境梯度上的排序参数提供了一种较好的交错带定量指标,样带植被数据特征参数的变异轮廓图能够反应植被沿样带的物种组成,结构和空间变化格局,可以反应植被沿环境梯度的β多样性和植物群落的梯度分化,植被变异侧面轮廓图的间断或不连续（突变）区间就是群落边界的位置。     

边缘效应的空间尺度与测度

综述了边缘效应的空间尺度类型以及在不同尺度上的测度方法.基于大量的研究整合,认为边缘效应空间尺度的划分,可以根据空间尺度的不同以及边缘效应形成和维持因素,分为大中小3个尺度类型,即大尺度的生物群区交错带、中尺度的景观类型之间的生态交错带和小尺度的斑块(生态系统)之间的群落交错区.大尺度主要是以植被气候带为标志的生物群区间的边缘效应,这种地带性的交错区主要受大气环境条件的影响.中尺度类型主要包括城乡交错带、林草交错带、农牧交错带等类型,是不同生态系统要素的空间交接地带,在物质能量等相互流动的作用下变得更为复杂.小尺度水平上是指斑块之间的交错所形成的边缘效应,受小地形等微环境条件及生物非生物等因子的制约,研究主要集中在群落边缘、林窗边缘和林线交错带等方面.对边缘效应测度的定量化研究有助于更加深入理解边缘效应.在大尺度水平上,边缘效应测度的研究主要是应用数量生态学等方法,研究不同气候带之间界线的划分及其物种分布的梯度规律性.中尺度水平上应用景观生态学的3S技术等方法,侧重于研究交错带的动态变化趋势及位置宽度的判定.小尺度水平上通过对距离边缘的长度,各群落中种群的数量、结构、多样性等定量指标的测定来构建测度公式,从而对边缘效应的强度进行量化,并反映边缘对群落的正负效应.总体上看,主要集中于中小尺度上,未来应该强化大尺度边缘效应测度的研究.     

The Role of Ecotones in Emerging Infectious Diseases

Recognition of the significance of the boundary between ecological systems, often referred to as the ecotone, has a long history in the ecological sciences and in zoonotic disease research. More recent research in landscape ecology has produced an expanded view of ecotones and elaboration of their characteristics and functions in ecosystems. Parallel research on emerging infectious diseases (EIDs) and the causes of increased rates of pathogen transmission, spread, and adaptation suggests a correspondence between ecotonal processes and the ecological and evolutionary processes responsible for zoonotic and vector-borne emerging infections. A review of the literature suggests that ecotones play a role in a number of the most important EIDs. Yet these are the only diseases for which specific landscape ecological information exists in the literature or disease reports. However, the similar disease ecologies of these with about half of the approximately 130 zoonotic EIDs suggests ecotones, particularly their anthropogenic origination or modification, may be generally associated with ecotones and the global trend of increasing EIDs.     

Spatial scale types and measurement of edge effects in ecology

Classification of spatial scales and measurement of edge effects in ecology were reviewed. The spatial scales can be classified into large scale (biome ecotone), meso-scale (ecological ecotone) and small scale (community ecotone) through the formation and maintenance of edge effects in ecology based on the synthetic analysis of published literatures. The biome ecotone is influenced by climate, regional dominant vegetation and terrain environment. The ecological ecotone is usually distributed in the transitional region with remarkable habitat heterogeneity. It connects adjacent ecosystems and affects the flow of energy and nutrient. Nowadays, study on edge effects in ecology mainly focuses on boundary sensitivity which associates with urban-rural ecotone, forest-grassland ecotone, agro-pastoral ecotone, forest-farmland ecotone, water-land ecotone and forest-swamp ecotone. As to the community ecotone which links with different patches to the interior of the community, previous studies focused on community edge, gap edge and treelines. The borderlines of different biome ecotones and the gradients of species distribution in the biome ecotones have been investigated through the method of quantitative ecology. The dynamic change, location and width of the ecological ecotone have been studied using the Geographic Information System (GIS), Remote Sensing (RS) and Global Positioning System (GPS) technologies and the landscape ecology theory. As important indicators, distance from edge, population, structure and diversity determined for establishing models can be applied to measure the intensity of edge effects and decide the positive or negative impact on communities. Although study on the edge effects in ecology was mostly reported at the meso-scale and small scale, study at large scale should be paid more attention as it is the potential value in ecology and global change fields.     

Tropical montane forest ecotones: climate gradients, natural disturbance, and vegetation zonation in the Cordillera Central, Dominican Republic

Aim We examined relationships between climate–disturbance gradients and patterns of vegetation zonation and ecotones on a subtropical mountain range. Location The study was conducted on the windward slopes of the Cordillera Central, Dominican Republic, where cloud forest appears to shift in a narrow ecotone to monodominant forest of Pinus occidentalis. Methods Climate, disturbance and vegetation data were collected over the elevation range 1100–3100 m and in 50 paired plots along the ecotone. Aerial photographs were georeferenced to a high‐resolution digital elevation model in order to enable the analysis of landscape‐scale patterns of the ecotone. Results A Shipley–Keddy test detected discrete compositional ecotones at 2200 and 2500 m; the distributions of tree species at lower elevations were continuous. The elevation of the ecotone determined with aerial photographs was fairly consistent, namely ± 164 m (SD) over its 124‐km length, but it exhibited significant landscape variation, occurring at a lower elevation in a partially leeward, western zone. The ecotone also occurred significantly lower on ridges than it did in drainage gullies. Ecotone forest structure and composition differed markedly between paired plots. In pine paired plots, the canopy height was 1.7 times higher and the basal area of non‐pine species was 6 times lower than in the cloud forest directly below. Fire evidence was ubiquitous in the pine forest but rare in the abutting cloud forest. Mesoclimate changed discontinuously around the elevation of the ecotone: humidity and cloud formation decreased markedly, and frost frequency increased exponentially. Main conclusions The discreteness of the ecotone was produced primarily by fire. The elevational consistency of the ecotone, however, resulted from the overarching influence of mesoclimate on the elevational patterns of fire occurrence. Declining temperature and precipitation combine with the trade‐wind inversion to create a narrow zone where high‐elevation fires extinguish, enabling fire‐sensitive and fire‐tolerant taxa to abut. Once established, mesotopography and contrasting vegetation physiognomy probably reinforce this boundary through feedbacks on microenvironment and fire likelihood. The prominence of the pine in this study – and of temperate and fire‐tolerant taxa in subtropical montane forests in general – highlights the importance of climate‐disturbance–biogeography interactions in ecotone formation, particularly where fire mediates a dynamic between climate and vegetation.     

Evidence on ecotone concepts from switch,environmental and anthropogenic ecotones

Abstract. Four contrasting ecotones were sampled to address three questions: (1) Are there ‘ecotonal’ species, (2) Do ecotones possess higher (or lower) species richness than the adjacent communities? and (3) Are exotic species more likely to occur in ecotones? One ecotone was edaphic, one was apparently caused by a positive‐feedback switch, one was environmental/anthropogenic and one was entirely anthropogenic. The exact position of each ecotone was established from the spatial change in ordination scores. Ecotonal species, in the sense of species mainly restricted to the ecotone at the site, were present in all four ecotones. All but one of the ecotonal species were native. The switch ecotone and the purely anthropogenic ecotone also contained native species that were significantly more frequent in the ecotone than in either adjacent community. Species richness was intermediate between that of the two adjacent communities in three of the ecotones. In the environmental/anthropogenic ecotone, species richness was higher than in adjacent communities, but not significantly so. There were appreciable numbers of exotic species in the two ecotones with anthropogenic influence, one of which had a proportion of exotic species intermediate between the two adjacent communities. Contrary to theory, the proportion of exotic species in the second ecotone was significantly lower than in either adjacent community. We conclude that all three features we examined depend on the particular ecological conditions and the ecology of the species present; they are not intrinsic properties of ecotones.     

Properties of ecotones: Evidence from five ecotones objectively determined from a coastal vegetation gradient

Abstract. Several properties have been suggested to be characteristic of ecotones, but their prevalence has rarely been tested. We sampled five ecotones to seek evidence on seven generalizations that are commonly made about ecotones: vegetational sharpness, physiognomic change, occurrence of a spatial community mosaic, many exotic species, ecotonal species, spatial mass effect, and species richness higher or lower than either side of the ecotone. The ecotones were in a sequence from scattered mangroves, through salt marsh, rush‐marsh, scrub, woodland, to pasture. We developed a method to objectively define, by rapid vegetational change, the position and depth of an ecotone, identifying five ecotones. Their positions were consistent across three sampling schemes and two spatial grain sizes. One ecotone is a switch ecotone, produced by positive feedback between community and environment. Another is anthropogenic, due to clearing for agriculture. Two others are probably environmental in cause, and one may be largely a relict environmental ecotone. Sharp changes in species composition occurred. Three ecotones were associated with a change in plant physiognomy. In two, the ecotone was located just outside a woodland canopy, in the zone influenced by the canopy. Community mosaicity was evident at only one ecotone. There were few strictly ecotonal species; many species occurred more frequently within ecotones than in adjacent vegetation, but there were never significantly more ecotonal species than expected at random. There was little evidence for the spatial mass effect reducing ecotonal sharpness, or leading to higher species richness within ecotones. Species richness was higher than in the adjacent habitat in only one ecotone. It seems that supposedly characteristic ecotone features depend on the particular ecological situation, and the ecology of the species present, rather than being intrinsic properties of ecotones.     

Measuring the abruptness of patchy ecotones – A simulation-based comparison of landscape pattern statistics

The use of statistics of landscape pattern to infer ecological process at ecotones requires knowledge of the specific sensitivities of statistics to ecotone characteristics. In this study, sets of patch-based and boundary-based statistics were evaluated to assess their suitability as measures of abruptness on simulated ecotone landscapes. We generated 50 realizations each for 25 groups of ecotones that varied systematically in their degree of abruptness and patchiness. Factorial ANOVA was used to evaluate the sensitivity of statistics to the known differences among the simulated groups. Suitability of each index for measuring abruptness was evaluated using the ANOVA results. The statistics were then ranked in order of their suitability as abruptness statistics based on their sensitivity to abruptness, the consistency of the relationship, and their lack of sensitivity to patchiness. The two best statistics for quantifying abruptness were those we developed based on lattice delineation methods, and are called cumulative boundary elements and boundary element dispersion. The results of this research provide support for studies of ecotone process that rely on the interpretation of patch or boundary statistics.     

长白山林区森林/沼泽交错群落的植物多样性

本研究应用样带网格调查方法,对森林／沼泽交错区上6种群落的植物多样性状况、优势种类与分布以及交错区环境梯度进行了研究。结果表明：森林／沼泽交错区植物多样性具有沿着交错区环境梯度逐渐增高的趋势;发育成熟的交错群落具有最高的植物多样性,且高于相对应的典型森林群落。由于交错区群落存在着沼泽植物类群、森林类群以及交错区群落的优势种类群,故发育成熟的交错区群落种类较丰富,一些优势种种群数量为森林中的5倍。因为交错区的生境对于满足这些种类的生活史具有重要作用。森林／沼泽交错群落的特征与交错区环境梯度以及两个植被类型的特征密切相关。     

松嫩平原西部生态脆弱带景观结构与生态耦合分析

研究了松嫩平原西部生态脆弱带生态景观结构,认为景观地球化学的空间分异及相互复合。决定了西部复杂而有规律的生态景观结构．景观地球化学梯度和生态梯度的耦合结果反映出大多植物沿景观地球化学梯度的生长状况表现为钟形或生态分布形曲线．现代条件下,西部植物群落的演替与土壤景观地球化学条件的改变几乎是同时发生的,二者在一定条件下互为因果关系.