一类食饵种群中具有传染病的捕食-被捕食系统

对疾病仅在食饵种群传播的有比例依赖的捕食-被捕食系统的动力学进行了分析,给出了每个平衡点附近系统的性态,定义了决定疾病灭绝和成为地方病的阁值R_0．得出的结论是:在比例依赖的捕食-被捕食系统中,染病食饵种群可以充当一个生物控制量,以抑制种群的绝灭．     

小鞘指环虫种群的聚集性研究

本文中建立了一个衡量聚集性的指标－聚集度Ａ,并用该指标结合方差／均数和负二项分布的参数ｋ值分析了小鞘指环虫（Ｄａｃｔｙｌｏｇｙｒｕｓｖａｇｉｎｕｌａｔｕｓ）种群在其宿主鲢（Ｈｙｐｏｐｈｔｈａｌｍｉｃｈｔｈｙｓｍｏｌｉｔｒｉｘ）种群中分布的聚集程度与感染率和丰度的关系。结果表明该虫种群的聚集程度随感染率及丰度的上升而呈现下降的特点,作为衡量聚集性的指标,聚集度要优于ｋ值,而后者又优于方差与均数之比,     

岛屿生物地理学与集合种群理论的本质与渊源

岛屿生物地理学和集合种群理论是目前生物多样性保育所依赖的主要生态学理论。人们通常强调这两种理论的区别,对它们之间的关联却很少注意到。事实上,这两种理论是同根同源的。以经典集合种群理论的创始者R．Levim对他与岛屿生物地理学的创始者R．H．MaeArthur的合作过程以及岛屿生物地理学对他提出集合种群理论的影响的回顾为基础,分析比较了岛屿生物地理学、经典集合种群理论、以Hanski为代表的现代集合种群理论的基本假设、研究范式和核心思想的异同,简要介绍了多物种集合种群与集合群落研究的差异,最后分析了岛屿生物地理学和集合种群理论在生物多样性保育实践中的应用和存在问题。     

具年龄结构的种群在破碎化生境中的空间分布模型

随着人类和其他生物赖以生存的环境破碎化程度的加剧,许多以前是连续分布的物种,目前不得不在破碎化生境(斑块)中求生存,所以,种群在破碎化生境(斑块)中分布问题的研究对生物保护和生境重建意义重大．本文运用Leslie矩阵和Markov链建立了一个具年龄结构的种群在破碎化生境中随时间动态变化的分布模型,讨论了种群在该生境中持续存在以及灭绝的条件．     

生长季节和非生长季节交替出现的种群动态模型及环境变化的影响

有些生物的生长季节和非生长季节交替出现,本文建立了描述这种生物种群动态的方程,并研究了在环境稳定、随机波动、定向变化的情况下种群的变化方式,还讨论了种群的危害及濒危情况．生长季节延长时种群增大,有害生物的危害加重,濒危生物濒危程度减轻;生长季节缩短时种群减小,有害生物的危害减轻,濒危生物更加濒危或灭绝．     

临界退偿系统的捕获优化问题

本文研究具有临界退偿特性生物种群的动力系统平衡点的稳定性,导出了获得最大持续产出的条件．阐述了临界退偿系统生物种群的脆弱性和保护措施及其投入产出关系．     

生物环及其测度

本文将一类生物种群抽象为“生物环”并定义了生物环上的测度,利用这一测度研究了两类生物种群的可测性．     

污染环境下单种群模型生存阈值

本论文研究了污染环境下毒素对单种群生存的影响。在环境容纳量较小的假设下建立了生物种群模型,在该模型中不但考虑了环境毒素浓度对生物个体生存的影响,还考虑了生物个体从食物链中吸收的毒素对其影响。通过研究得到种群一致持续生存和若平均持续生存的充分条件,同时得到种群持续生存依赖于模型参数和生物个体体内毒素净化率的某些充分条件．     

利用RAPD-PCR方法鉴定我国烟粉虱的生物型

收集了国内北京、山东、广东和海南等14个省市23个地区的蔬菜、园林花卉和杂草上的23个烟粉虱Bemisia tabaci (Gennadius)种群,根据报道合成了一个随机引物H₁₆,运用RAPD-PCR技术对所收集的烟粉虱种群进行了生物型鉴定。结果表明在23个烟粉虱种群中,有17个种群同属于危害严重的“B生物型”,这些种群主要分布在交通便利的城市或沿海地区,而非B生物型则主要分布在交通不便的山区或内陆。对烟粉虱B生物型的分布与寄主植物和环境条件进行了初步的探讨。     

池鹭繁殖种群数量、活动规律和生物生产量的研究

本文报道池鹭种群数量变动,种群活动,雏鸟生长和生物生产量。种群活动可划分为适到期,运情期,繁殖期,同鸟活动期,集群活动和迁离期。１９９０,１９９１二年繁殖前种群密度分别为１３００只／ｈｍ＾２和１４０１只／ｈｍ＾２,繁殖后增加密度为２０８７只／ｈｍ＾２和２２４８只／ｈｍ＾２。雏鸟体重增长曲线议程为：Ｗ＝２８６／１＋ｅ＾－０．４０９（ｔ－１２．６）１９９０,１９９１年繁殖种群的生物生产量分别为１９７．     

闽东北海域中华管鞭虾种群聚集特性

以负二项参数、平均拥挤度和聚块指数为种群分布格局强度指标,分析了闽东北海域中华管鞭虾(Solenocera crassicornis)种群聚集特性,探讨了种群聚集特性的驱动因子。结果表明,中华管鞭虾种群聚集强度较强,个体平均拥挤度较高,种群主要集中于少数团聚的斑块,不同季节种群聚集特性差异显著,春季,种群聚集强度较强,个体平均拥挤度最低,种群主要由单一团聚的斑块组成;夏季,种群聚集强度较弱,个体平均拥挤度高,种群主要由4个斑块组成;秋季,种群聚集强度最弱,个体平均拥挤度较低,种群主要由7个斑块组成;冬季,种群聚集强度最强,个体平均拥挤度最高,种群主要由单一团聚的大斑块组成。随着个体生长速度的增大,种群呈现扩散的趋势,饵料浮游动物生物量和底层水温是影响种群聚集强度的主要因子。     

秦岭大熊猫种群扩散格局及研究方法

种群扩散格局是研究种群扩散规律和机制的关键信息,也是制定物种保护对策的重要基础。大型动物种群扩散格局研究方法为扩散生态学研究的薄弱领域,并制约扩散生态学的发展。以秦岭大熊猫为研究对象,根据2000年以来的种群调查数据,基于大熊猫领域的特性,利用GIS的扩展区分析功能和景观分析方法研究了大熊猫种群分布区及动态;基于聚集的特性,利用GIS的核密度分析功能对大熊猫种群多度和聚集状况及空间变化进行了分析。发现2012年的秦岭大熊猫种群分布区较2000年增加5.5%(即15307.8hm~2),高密度种群聚集区从2处变成1处,种群聚集程度进一步增加、聚集格局的完整性大大提升,尤以中密度聚集区增长最显著,种群格局呈明显的分布区扩张、聚集度增加的态势。表明基于物种的生物学特性,立足于种群分布和多度格局变化,通过长期调查和监测可以有效掌握物种的种群扩散格局;大型动物可根据其生物学特性探索可行的方法与量化种群扩散的参数来研究其扩散格局,从而促进大型动物种群扩散研究的开展。     

温室瓜蚜种群动态的研究

瓜蚜AphisgossypiiGlover在温室黄瓜上的空间格局为聚集分布,分布的基本成分为个体群,聚集强度随密度的上升而下降;瓜蚜主要分布于中部和下部叶片。瓜蚜在温室黄瓜上呈指数增长,模型为Nt=0.1745e0.7414t(r=0.9676)。应用最优分割法将瓜蚜种群动态划分为3个阶段:初建期、发展期和高峰期。在种群初建期,有翅蚜开始迁入,数量较低,以扩散为主,分布不均匀,聚集强度较高;在发展期,瓜蚜种群不断繁殖扩散,分布日趋均匀,聚集强度逐渐下降;在高峰期,瓜蚜种群数量急剧增长到最高峰,分布至所有植株,聚集强度继续下降,此阶段后由于黄瓜植株受害枯萎,瓜蚜缺少食物而数量急剧下降。     

Determinants of helminth aggregation in natural host populations: individual differences or spatial heterogeneity?

We assessed the importance of spatial heterogeneity for the aggregation of helminth populations in the bank vole Clethrionomys glareolus (Arvicolinae) using a previously published method which allows to analyse parasite aggregation at two host population levels, i.e., within and between spatial samples of the host population.
In the main empirical material from Finnish Lapland (Pallasjärvi), all five helminth species were significantly aggregated within study sites, but only three rare species showed significant aggregation among sites. In all helminth species, the total aggregation was primarily (79-98%) determined by aggregation within sites, i.e., between host individuals. Despite the larger spatial scale and more heterogeneous landscape, the comparative material from South Finland (Luhanka) supported the generally high proportion of the total aggregation due to within-site heterogeneity.
Despite the clear interspecific differences in patchiness of helminth populations, the proportion of the total aggregation due to among-site heterogeneity did not vary significantly among helminth species. The results indicate a link between aggregation at two population levels; species that showed strong within-site aggregation were also characterised by pronounced spatial heterogeneity and significant among-site aggregation.     

Aggregation and regularity: an inclusive one-tailed nearest-neighbour analysis of small spatially patchy populations

When analysing spatial pattern, aggregation and regularity are normally regarded as being mutually exclusive and a two-tailed test is applied to check whether or not there is a deviation from random expectation towards one or the other. However any fine-scale regularity occurring in crowded patches is likely to be masked by the larger-scale aggregation using this approach. An associated problem is that edge effects are particularly severe for small patchy populations. An inclusive analysis utilising one-tailed nearest-neighbour tests to check for aggregation and regularity separately is described. In addition the technique resolves the edge-effect problem. The approach is illustrated using a synthetic patchy population, and is then applied to a population of granite tors showing both large-scale aggregation and fine-scale regularity. Regular spacing of buzzard territories is discussed briefly.     

玉米田截形叶螨种群动态的研究

1999～2001年于内蒙古巴彦卓尔盟杭锦后旗研究了玉米田截形叶螨田间种群动态。结果表明．截形叶螨在玉米田的空间格局为聚集格局,随着叶螨种群密度的上升,其聚集强度下降应用最优分割法将玉米截形叶螨田间种群动态划分为5个阶段：①7月上旬前为种群初建期,叶螨在玉米田刚开始发生,种群数量很低,只分布在极少数植株上;②7月中旬为种群缓慢增长期,种群数量低,增长缓慢,聚集强度高;③从7月下旬至8月中旬为种群快速增长期,种群数量高,增长迅速,叶螨分布至全田,聚集强度下降;④8月下旬为种群高峰期,种群数量最高,聚集强度较低;⑤9月以后为玉米截形叶螨种群的衰落期,由于玉米受害严重及玉米进入生长后期,中下部叶片大部分均已枯死,上部叶片也已老化营养水平下降,加之气温下降,叶螨种群数量迅速下降。     

Plasma membrane lipid packing and leukocyte function-associated antigen-1-dependent aggregation of lymphocytes

A simple model system for study of adhesion mediated by leukocyte function-associated antigen-1 (LFA-1) is aggregation of lymphocytes stimulated in vitro. Although aggregation is blocked by monoclonal antibodies to LFA-1, not all lymphocytes expressing LFA-1 aggregate, indicating that LFA-1 is necessary but not sufficient for aggregation. To investigate whether the lipid bilayer plays a role in the functional activation of LFA-1, human peripheral blood lymphocytes and murine splenic lymphocytes were stimulated in culture, and measurements made of aggregation vs. packing of plasma membrane lipids. Progression of cells into aggregates was paralleled by a decrease in lipid packing of the population as a whole, as monitored by increased staining with the fluorescent probe merocyanine 540. Cells from aggregates stained more intensely than nonaggregated cells from the same population, indicating that aggregates are preferentially formed from cells in the population with the loosest packed membrane. In contrast, aggregated cells were found to express equivalent or even lower amounts of LFA-1 than nonaggregated cells. Looser lipid packing is therefore associated with the development of LFA-1-dependent aggregation, and might be involved in the functional activation of this cell adhesion molecule. © 1993 Wiley-Liss, Inc.     

The mechanistic basis of discrete-time population models: The role of resource partitioning and spatial aggregation

The purpose of this paper is to present a unified view to understand mechanistic basis of various discrete-time population models from the viewpoints of resource partitioning and spatial aggregation of individuals. A first-principles derivation is presented of a new population model which incorporates both scramble and contest competition using a site-based framework in which individuals are distributed over discrete resource sites. The derived model has parameters relating to the way of resource partitioning and the degree of spatial aggregation of individuals, respectively. The model becomes various population models in various limits in these parameters. This model thus provides a unified view to understand how various population models are interrelated. The dependence of the stability of the model on the parameters is also examined.