生境破碎化对动物种群存活的影响

生境破碎是生物多样性下降的主要原因之一。通常以岛屿生物地理学、异质种群生物学和景观生态学的理论来解释不同空间尺度中生境破碎化的生态学效应。生境破碎化引起面积效应、隔离效应和边缘效应。这些效应通过影响动物种群的绝灭阈值、分布和多度、种间关系以及生态系统过程,最终影响动物种群的存活。野外研究表明,破碎化对动物的影响,因物种、生境类型和地理区域不同而有所变化,因此,预测物种在破碎生境中的存活比较困难。研究热点集中于：确定生境面积损失和生境斑块的空间格局对破碎景观中物种绝灭的相对影响,破碎景观中物种的适宜生境比例和绝灭阈值,异质种群动态以及生态系统的生态过程。随着3S技术的发展,生境破碎化模型趋于复杂,而发展有效的模型和验证模型将成为一项富有挑战性的任务。     

农业生态系统杂草多样性保持的生态学功能

杂草是农业生态系统中的重要生物组成部分 ,也是影响农林作物生长和导致产量下降的重要因素之一。过去人们一直努力将杂草从农业生态系统地中清除出去 ,对杂草的研究往往也更多地注重其危害性和防治途径。近年来保护农业生产区域中杂草等野生植物的多样性以及发挥其在维持生态平衡中的作用逐渐为人们所重视[1～4] 1) ,2 ) 。本文对国内外有关农业生态系统中杂草多样性保护及其生态学功能的研究报道作一简要概述 ,以供参考。1　农业生态系统杂草多样性保护早在 1 982年Ｈｉｂｉｇ提出不使用除草剂、不铲除杂草等办法保持农田周围、草地、园林…     

城市生态园林与生物多样性保护

城市生态园林与生物多样性保护袁兴中,刘红（曲阜师范大学,２７３１６５）ＵｒｂａｎＥｃｏｌｏｇｉｃａｌｇａｒｄｅｎｉｎｇａｎｄＢｉｏｄｉｖｅｒｓｉｔｙＣｏｎｓｅｒｖａｔｉｏｎ．￥ＹｕａｎＸｉｎｇｚｈｏｎｇ;ＬｉｕＨｏｎｇ（Ｄｅ－ｐａｒｔｍｅｎｔｏｆＢｉ...     

中国西部干旱地区啮齿动物多样性分布格局

在系统整理我国西部干旱地区啮齿动物的分布资料,获得物种分布范围的基础上,应用GIS软件,基于等面积栅格系统,研究啮齿动物的等级多样性,探讨啮齿动物物种的区域分化特征。结果表明,祁连山地和北塔山、伊犁天山、阿拉套山和阿尔泰山地,以及贺兰山地等处的啮齿动物的属数最高;塔里木盆地中心和藏北高原的属数最低。阿尔泰山南麓、伊犁天山和东祁连山地的啮齿动物科数最多;塔里木盆地中心和藏北高原的科数较少。在青藏高原的周边,寒漠与温性荒漠、荒漠与山地、高原与盆地、荒漠与草原、山地与草原等景观的交界处,多样性指数较高。蒙新荒漠区的啮齿动物的属科数比相对较高,青藏高原的属科数比值较低,但青藏高原的种属数比值相对较高,而且GF指数亦较高。     

青藏高原高寒草甸植被特征与温度、水分因子关系

以广布于青藏高原的高寒草甸为研究对象,进行模拟增温实验,探讨高寒草甸植被特征与温度、水分因子关系,并试图论证高寒草甸植被是否符合生物多样性代谢理论.结果表明:①高寒草甸植被物种多样性的对数与绝对温度的倒数呈显著线性递减关系,空气-地表-浅层土壤(0-20 cm)温度(R2 ＞0.6,P＜0.01)较深层土壤(40-100 cm)温度(R2＜0.5,P＜0.05)对物种多样性影响大;其植被新陈代谢平均活化能为0.998-1.85 eV,高于生物多样性代谢理论预测值0.6-0.7 eV,这是高寒草甸植被对长期低温环境适应进化的结果.②除趋势对应分析和冗余分析显示,温度对植被地上部分影响较大,而土壤水分对全株影响均较大,适当的增温与降水均可极显著促进高寒草甸植被生长.③逐步回归和通径分析显示,40 cm、60 cm深度土壤水分对植被地上部分产生直接影响,20 cm高度空气相对湿度和40 cm深度土壤温度对其产生间接影响;40 cm深度土壤温度和60 cm深度土壤水分对植被地下部分产生直接影响,红外地表温度对其产生间接影响.深层土壤温度和水分对高寒草甸植被具有影响作用,这可能与增温后冻土的融化有关,但其机理尚待进一步研究.     

Intraspecific diversity of the Cassava Green Mite Mononychellus progresivus (Acari: Tetranychidae) using comparisons of mitochondrial and nuclear ribosomal DNA sequences and cross-breeding

Intraspecific diversity in Cassava Green Mite Mononychellus progresivus Doreste was examined using individuals collected in Benin and the Congo and in Columbia and Brazil. Comparisons were based on mitochondrial and ribosomal DNA sequences and the results of several cross-breeding experiments. Sequence variation was examined in a total of 1139 base pairs (bp) constituting the ITS2 ribosomal DNA (805 bp) and a fragment of the Cytochrome Oxidase I (COI) gene (334 bp). Sequence divergence is low, ranging from 0% to 2.1% for COI and from 0% to 0.4% for ITS2. Inter-strain comparisons have shown that the two African populations appear to be identical. They were similar to the Colombian population while the Brazilian population was clearly different. The data support the hypothesis of a single introduction of the species in the two African populations. Crossing experiments have shown partial hybrid sterility, suggesting a genetic incompatibility consistent with differences detected by sequence data. The results show the usefulness of molecular markers as a tool for determining taxonomic status and dispersion paths in spider mites.     

中国东北样带(NECT):十年集成与未来挑战

Northeast China Transect (NECT), one of the fifteen International Biosphere-Geosphere Programme (IGBP) terrestrial transects, has been established for 10 years by Prof. Zhang Xin-Shi, through a core project of the IGBP - the Global Change and Terrestrial Ecosystems (GCTE). This transect is located in the mid-latitude semi-arid region, ranging 42-46°N latitude and 110-132癊 longitude. The primary driving force for global change is precipitation and the secondary one is land use intensity. Research progresses have been performed during the past decade in the following aspects: ecological database development, climate and its variability, ecophysiological response of plants to environments, vegetation and landscape changes, biodiversity patterns and their changes, plant functional types and traits with relation to climatic gradient, productivity and carbon dynamics, pollen-vegetation relationship, trace gas emissions, land use and land cover changes, as well as biogeographical and biogeochemical modelling. In order to achieve the higher level of integrated research, the NECT needs the consistent basic data sets within the same framework, further field experiments and observations, integrated simulations of vegetation structure, process and function from patch, landscape to biome scales, intercomparisons of results and simulations within the transect and to other IGBP transects, multidisciplinary research, national and international co-ordinates, and full scientific plan and implementation strategy.     

卧龙自然保护区针阔混交林林隙更新规律

卧龙自然保护区五一棚大熊猫野外观测站周围的针阔混交林由于历史原因破坏严重,长期以来自然恢复较差。为调查该区林隙更新的现状及其影响因素,作者采用林隙样线调查方法研究了该区针阔混交林林隙更新规律。结果显示,历史上的自然干扰与人为干扰共同影响着该区林隙更新的格局和特征,林隙天然更新受环境因素制约,更新规律表现为:更新幼苗的种类较形成木的种类丰富,更新乔木幼苗的优势度排序与形成木不同;林隙主要树种的更新受各类环境因子的影响而存在差异,桦木(Betula spp.)更新受地形影响较大,岷江冷杉(Abies faxoniana)受土壤因素影响显著,杜鹃(Rhododendron spp.)更新则受地形因子和林隙形成木的特征影响显著;更新物种的多样性指数均表现出受土壤因子的影响显著。由此推测,林隙大小并非影响该区林隙更新的关键因素,而土壤因素可能是制约优势树种天然更新和更新物种多样性的重要原因之一。     

Key Elements in a Framework for Land Use Impact Assessment Within LCA (11 pp)

Background, Aim and Scope Land use by agriculture, forestry, mining, house-building or industry leads to substantial impacts, particularly on biodiversity and on soil quality as a supplier of life support functions. Unfortunately there is no widely accepted assessment method so far for land use impacts. This paper presents an attempt, within the UNEP-SETAC Life Cycle Initiative, to provide a framework for the Life Cycle Impact Assessment (LCIA) of land use. Materials and Methods: This framework builds from previous documents, particularly the SETAC book on LCIA (Lindeijer et al. 2002), developing essential issues such as the reference for occupation impacts; the impact pathways to be included in the analysis; the units of measure in the impact mechanism (land use interventions to impacts); the ways to deal with impacts in the future; and bio-geographical differentiation. Results: The paper describes the selected impact pathways, linking the land use elementary flows (occupation; transformation) and parameters (intensity) registered in the inventory (LCI) to the midpoint impact indicators and to the relevant damage categories (natural environment and natural resources). An impact occurs when the land properties are modified (transformation) and also when the current man-made properties are maintained (occupation). Discussion: The size of impact is the difference between the effect on land quality from the studied case of land use and a suitable reference land use on the same area (dynamic reference situation). The impact depends not only on the type of land use (including coverage and intensity) but is also heavily influenced by the bio-geographical conditions of the area. The time lag between the land use intervention and the impact may be large; thus land use impacts should be calculated over a reasonable time period after the actual land use finishes, at least until a new steady state in land quality is reached. Conclusions: Guidance is provided on the definition of the dynamic reference situation and on methods and time frame to assess the impacts occurring after the actual land use. Including the occupation impacts acknowledges that humans are not the sole users of land. Recommendations and Perspectives: The main damages affected by land use that should be considered by any method to assess land use impacts in LCIA are: biodiversity (existence value); biotic production potential (including soil fertility and use value of biodiversity); ecological soil quality (including life support functions of soil other than biotic production potential). Bio-geographical differentiation is required for land use impacts, because the same intervention may have different consequences depending on the sensitivity and inherent land quality of the environment where it occurs. For the moment, an indication of how such task could be done and likely bio-geographical parameters to be considered are suggested. The recommendation of indicators for the suggested impact categories is a matter of future research.