黄河下游农业景观中不同生境类型地表节肢动物优势类群

生物多样性是连接景观异质性与生态系统服务的桥梁。在区域尺度上,以指示类群代替地表节肢动物类群,可以有效的开展生物多样性的保护工作。但是,在黄河下游农业景观中,关于地表节肢动物指示类群的研究报道较少。以黄河下游农业景观中4种生境类型(农田、林地、树篱和沟渠)为研究样地,且在农田生境中划分不同尺度(尺度1,3.6 hm2、尺度2,14 hm2和尺度3,28 hm2),通过调查不同生境中地表节肢动物分布及其多样性,结合地表节肢动物优势类群的辨识,分析了优势类群和地表节肢动物多样性的相关性,确定了研究区内地表节肢动物多样性的指示类群。结果发现:研究区内地表节肢动物优势类群为膜翅目、鞘翅目和蜘蛛目。树篱和林地生境的地表节肢动物多样性指示类群是膜翅目,农田生境中地表节肢动物多样性指示类群是鞘翅目,沟渠生境中地表节肢动物多样性指示类群是蜘蛛目。农田生境中优势类群间无相关性(P0.05);林地、沟渠和树篱生境中鞘翅目与蜘蛛目之间存在显著正相关(P0.01);林地和沟渠生境中,鞘翅目与膜翅目之间存在正相关(P0.05)。在农田生境中优势类群之间的相关性存在尺度依赖性,随着空间尺度的增大,相关性有一定的增强。在尺度2和尺度3上膜翅目和鞘翅目均存在正相关(P0.05),并且随着尺度增加而呈上升趋势。研究表明,黄河下游农业景观中不同生境类型地表节肢动物多样性的指示类群差别较大,其中树篱和林地生境具有较高的相似性,而农田生境地表节肢动物优势类群相关性存在尺度依赖性。在黄河下游农业景观中,以优势类群多样性代替地表节肢动物类群的多样性,可以在条件不足、时间紧迫的情况下更加有效的开展生物多样性的保护工作。     

农业景观异质性对地表节肢动物多样性影响的最优尺度分析

农业景观均质化与破碎化是近代农田生物多样丧失的重要原因之一.为明确景观异质性对地表节肢动物多样性的影响,对下辽河平原典型农区——昌图县地表节肢动物多样性与不同尺度景观异质性进行相关性分析.结果表明:1000 m为研究景观指数对农田地表节肢动物多样性影响的最优尺度;地表节肢动物Simpson多样性指数与景观香农多样性指数...     

不同干扰背景下景观指数与物种多样性的多尺度效应——以巩义市为例

以黄河中下游山地丘陵区的巩义市为研究区,采用典型样地法对灌草丛、人工林和农田边缘3种不同干扰背景下的自然、半自然生境内的植物进行调查。基于景观生态学原理,在地理信息系统技术支持下,借助于Fragstatta3.3软件,以调查样地为中心,计算了150、250、500、750、1000、1250、1500m不同半径缓冲区内表征景观形状(Edge and patch shape)、边缘对照(Edge contrast)、相似度和邻近度(Proximity and similarity)、景观多样性(Diversity)、基质(Texture)、斑块大小和密度(Patch size and patch density)共6类52个指数,运用冗余分析(RDA)筛选出不同尺度下对该区农业景观中植物多样性有显著影响的景观指数。结果表明:不同尺度,景观指数对物种多样性的影响变化显著。灌草丛生境,在500—750m范围内,SHAPE_AM指数和PARA_AM指数能够很好的解释物种多样性,解释量为33.6%;人工林生境,SHAPE_AM指数、AREA_CV指数、SIMI指数和PAFRAC指数在1000—1250m范围内对物种多样性的解释量达到48.1%;农田边缘生境,GYRATE_CV指数、ENN_CV指数、PARA_MN指数和FRAC_AM指数在750—1250m范围内对物种多样性影响显著,解释量为32%。其中,辛普森多样性指数(SIDI)与灌草丛物种多样性在750—1250m范围内作用显著,ENN_CV指数仅对农田边缘物种多样性影响较大。景观指数对物种多样性的影响具有尺度依赖性,未来应全面综合探讨这些指数的尺度效应及在景观生态学中的应用。     

黄河下游平原非农植物多样性拆分研究

非农生物多样性的存在是农业景观生态系统健康持续发展的基础,对农业景观非农生境中植物群落物种多样性特征分析将有助于可持续农业景观构建措施的科学提出。在黄河下游平原典型农业景观中采用栅格分区的方式布设样点(共54个),采用典型样地法对各样点内的林地、树篱、田间道路和沟渠等主要非农生境的植物群落进行调查,采用生物多样性加性分配的方法探讨不同空间尺度上生物多样性的组成特征。结果显示:(1)各非农生境间植物群落物种多样性特征存在较大的差异。(2)偶见种从数量上构成了各非农生境中植物物种丰富度的主体,而常见种则行使着群落优势种和构建者的角色。(3)总体上,β多样性在各空间尺度中均对总物种丰富度具有重要贡献。(4)常见种和偶见种中物种组成格局存在显著差异:常见种的物种丰富度主要由α多样性贡献,而β多样性则贡献了偶见种的绝大部分。简言之,β多样性对区内植物多样性的保护和维持意义重大,农业景观中非农生境类别的出现对总物种丰富度的提高具有重要作用;各生境中较高的样点间β多样性(β样点)意味着在看似均质化的农业景观背景中依然具有较高的区域差异;景观组成和构型的变化将对农业景观中植物群落特征和物种多样性产生重要影响,且对偶见种的影响更甚。未来,应从景观和区域等更大尺度上,基于农业景观生态系统功能和服务的综合考虑及可持续农业景观的建立来探讨农业活动与生物多样性保护的权衡。     

宏生态尺度上景观破碎化对物种丰富度的影响

生物多样性的地理格局及其形成机制是宏生态学与生物地理学的研究热点。大量研究表明,景观尺度上的生境破碎化对物种多样性的分布格局具有重要作用,但目前尚不清楚这种作用是否足以在宏生态尺度上对生物多样性地理格局产生显著影响。利用中国大陆鸟类和哺乳动物的物种分布数据,在100 km×100 km网格的基础上生成了这两个类群生物的物种丰富度地理格局,进一步利用普通最小二乘法模型和空间自回归模型研究了物种丰富度与气候、生境异质性、景观破碎化的相关关系。结果表明,景观破碎化因子与鸟类和哺乳动物的物种丰富度都具有显著的关联关系,其方差贡献率可达约30%—50%(非空间模型)和60%—80%(空间模型),略低于或接近于气候和生境异质性因子。方差分解结果显示,景观破碎化因子与气候和生境异质性因子的方差贡献率的重叠部分达20%—40%。相对鸟类而言,景观破碎化对哺乳动物物种丰富度的地理格局具有更高的解释率。     

农业景观非农生境植物多样性及其影响因素

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。     

长期围封对疏勒河源区高寒草甸地表节肢动物多样性的影响

围封会促进退化高寒草甸植被和土壤环境恢复,长期围封也会导致生物多样性及其功能下降,影响高寒草甸生态系统的稳定,但这种影响会随着季节和生境条件变化而异。为了探究不同退化程度高寒草甸地表节肢动物群落变化对围封禁牧的响应,利用陷阱法调查了疏勒河源区沼泽化草甸、草甸和草原化草甸3种不同退化梯度高寒草甸围封禁牧和自由放牧处理下地表节肢动物群落结构变化。结果表明：围封禁牧对高寒草甸地表节肢动物群落组成及多样性的影响随生境条件不同而异。禁牧降低了沼泽化草甸地表节肢动物的物种丰富度,而提高了草甸和草原化草甸地表节肢动物的物种丰富度;围封禁牧对沼泽化草甸地表节肢动物群落结构影响较小,显著降低了草甸生境地表节肢动物活动密度、提高了地表节肢动物多样性和均匀度,相反,禁牧显著提高了草原化草甸生境地表节肢动物活动密度、降低其多样性和均匀度;豹蛛属1种是高寒草甸主要的地表节肢动物类群（相对多度为67.0%）,高寒草甸土壤水分有效性等生境条件不同影响了豹蛛属1种对围封禁牧的响应模式,进而影响了地表节肢动物群落结构变化。总之,高寒草甸退化程度影响了地表节肢动物多样性对禁牧和放牧的响应模式,沼泽化草甸适度放牧有利于提高地表节肢动物多样性及其功能。     

北京昌平区景观复杂度和局地管理对苹果园传粉蜂多样性的影响

传粉蜂为作物生产和粮食安全提供重要的生态系统服务。随着农业经济的不断发展,土地利用强度加剧,大量自然或半自然生境已经转变为农业用地。景观均质化和集约化管理导致野生蜂多样性下降,从而威胁到农业可持续生产。本研究以北京市昌平区苹果园为对象,探究景观复杂度(半自然生境比例)、局地管理强度(地表开花植物多样性和土壤全氮)及其交互作用对传粉蜂多样性的影响。结果表明: 共捕获传粉蜂8642头,其中人工蜂5125头,野生蜂分属5科14属49种3517头。传粉蜂多样性对景观复杂度和局地管理强度响应的最优尺度在500 m。样点半径500 m范围内,总传粉蜂和野生蜂多度随周围半自然生境增加均呈显著上升趋势。景观复杂度与开花植物多样性的交互作用对总传粉蜂和野生蜂物种丰富度有显著影响。当景观复杂度较低时(≤29.9%),总传粉蜂和野生蜂物种丰富度与开花植物多样性呈显著正相关;而当景观复杂度较高时(>29.9%),总传粉蜂和野生蜂物种丰富度与开花植物多样性呈显著负相关。此外,人工蜂多度随果园内局地开花植物多样性和土壤全氮增加呈显著升高趋势。土壤全氮与开花植物多样性的交互作用对人工蜂多度有显著影响。当土壤全氮含量较低时(≤1.9 g·kg^-1),人工蜂多度与开花植物多样性呈显著正相关;而当土壤全氮含量较高时(>1.9 g·kg^-1),人工蜂多度与开花植物多样性呈显著负相关。农业景观中半自然生境比例的增加有利于提高野生蜂多度,而地表开花植物多样性可以促进传粉蜂多样性,但是受到景观尺度(半自然生境比例)和局地尺度(氮肥施用)的影响。因此,农业景观中野生蜂多样性的维持需要综合考虑多尺度因素来制定保护策略。尽可能保留更高比例的耕地仍然是生产的长期需求,而保持中等景观复杂度,增加地表开花植物多样性,减少氮肥施用量将是促进苹果园传粉蜂多样性的有效方式。     

小尺度下柠条林破碎化生境对地表甲虫多样性的影响

一般认为,景观斑块面积和破碎化对物种丰富度和分布格局有重要的影响。在宁夏中部荒漠地区,天然柠条林和人工柠条林地交错排列,形成点、片、带状等大小不等的斑块性分布,表现为典型的破碎化斑块格局生境特征。本文采用巴氏罐诱法调查了在小尺度下荒漠景观人工柠条林破碎化生境不同斑块内地表甲虫的物种多样性。结果共获得10科20属29种地表甲虫,其中拟步甲科昆虫占绝对优势,阿小鳖甲Microdera kraatzi alashanica Skopin、克小鳖甲Microdera kraatzi kraatzi(Reitter)为优势种。Rarefaction曲线显示较大面积的斑块有较多的物种多样性,但群落多样性指数各斑间块差异不显著。利用斑块面积对物种数-个体数进行回归分析表明,地表甲虫的物种多样性受斑块面积的影响,生境破碎化会导致地表甲虫多样性下降。     

复合茶园节肢动物类群特征值关系研究

为深入了解影响茶园节肢动物群落多样性的因子,本文对在茶园地面种植长节耳草Hedyotis uncinella Hook & Arn(茜草科,耳草属)的复合茶园茶树生境节肢动物类群多样性指数、物种丰富度、类群均匀度、物种优势度指数和类群优势集中性指数5个主要特征值之间的关系进行了因子分析与通径分析。结果显示:茶树生境节肢动物类群5个主要特征值可综合为三个主份量。第一主份量代表类群多样性指数和均匀性;第二主份量集中体现物种丰富度;第三主份量代表优势度指数,它们对方差的贡献率分别为50.279%、26.920%和22.466%。复合茶园节肢动物类群多样性与节肢动物类群丰富度和天敌类群丰富度呈极显著的正相关,而同类群优势集中性呈极显著的负相关。因此,要提高茶园节肢动物类群的多样性可通过营造复合茶园生境来增加节肢动物类群物种丰富度和天敌类群物种丰富度而减少物种优势集中性来实现。     

Landscape context determinants to plant diversity in the permanent meadows of Southern European Alps

In the Southern Alps, the role of landscape context on meadows plant diversity was evaluated using a multi-model information theoretic approach and five competing hypotheses of landscape context factors: habitat quality (H1), matrix quality (H2), habitat change (H3), matrix quality change (H4) and topography-environmental conditions (H5)- measured at three spatial scales (125, 250 and 500 m). Shannon diversity index and species richness represented plant diversity obtained in 34 plots (100 m² size). Landscape context affected plant diversity measures differently. Matrix quality change at larger scale (500 m) was the most supported hypothesis explaining Shannon diversity index, while species richness responded mostly to topography-environmental conditions in the immediate surroundings (125 m). No effects of present-day habitat and matrix quality (H1 and H2) were found. Matrix quality change affected positively Shannon diversity index through an effect of landscape neighbourhood context on farming management practices. Due to the importance of exposure and inclination of slopes, topography-environmental conditions influenced species richness mostly through energy-driven processes and farming management strategies. In terms of scale, matrix quality change was the strongest hypothesis explaining Shannon diversity index at all scales, while the underlying process affecting species richness changed with scale (H5 or H3). Overall, landscape context explained only 25–28 % of the variation in plant diversity, suggesting that landscape management may support biodiversity conservation when comprised in a global strategy including farming practices. In the study area, change in landscape diversity may be a good indicator for Shannon diversity index and south-eastern facing meadows should be preserved.     

Landscape-level effects on cynipid component communities of “orphaned” native shrubs

Native plants that persist in agricultural landscapes can be important for conserving and re-connecting fragmented biological communities, particularly to arthropods that live in and on them. However, their value as habitat may depend upon landscape context, which can differently impact species among trophic levels. We examined the communities of gall-inducing cynipid wasps and their parasitoids associated with a native wild rose, Rosa woodsii, in the Palouse region of southeastern Washington State and adjacent Idaho, to determine how this arthropod community varies with the landscape context of the host plant. Nine species of gall wasps (Diplolepis spp.), 11 species of parasitoids, and the inquiline cynipid, Periclistus sp. were sampled from R. woodsii shrubs throughout the Palouse region. We examined whether any gall-inducing cynipids were absent from R. woodsii in particular landscape contexts. We tested the relationship between community structure and landscape variables including landscape diversity and the proportion of prairie, agriculture, introduced grasslands, and built environments. All gall-inducer species occurred in every landscape context, although some species were more common on roses within prairie remnants. Gall-inducer and parasitoid species richness was positively correlated with the proportion of prairie in the landscape at radii from 100 to 1,500 m, with the scale of this effect differing between the two sample years. Landscape diversity had little or no effect on species richness. These results suggest that although R. woodsii supports diverse arthropod communities throughout a fragmented landscape, its greatest conservation potential will be realized if prairie remnants are conserved as well.     

Conservation of arthropod diversity in montane wetlands: effect of altitude, habitat quality and habitat fragmentation on butterflies and grasshoppers

1. The patterns of arthropod diversity were investigated in 24 montane wetlands in Switzerland. These differed in altitude, management regime (cattle-grazing vs. mowing), vegetation structure (index combining vegetation height and density) and degree of habitat fragmentation.
2. The general arthropod diversity was determined by net sampling at 10 sampling points per site. The diversity of grasshoppers and butterflies was measured by counting species richness at the site and species density (species richness per unit area) on transects. The species richness of grasshoppers and butterflies was found to be more sensitive to the geographical attributes of the site whereas species density was more affected by the habitat quality.
3. Grasshopper diversity decreased within the observed altitudinal range (800–1400 m) and was higher at grazed sites, whereas butterfly diversity was higher at mown sites. Arthropod diversity but not abundance of arthropods was positively related to the vegetation structure.
4. The species richness of butterflies was negatively influenced by the degree of habitat fragmentation: both the size of habitat as well as the area of wetland habitats within 4 km were related positively to the number of specialist wetland butterflies.
5. Late mowing as well as low-density cattle-grazing are appropriate management actions to maintain arthropod diversity in montane wetlands. In order to establish site-specific management plans, the biology of the present target species as well as the historical context should be considered.
6. We suggest that the best protection for the species examined in this study would be a network of wetland sites managed using a variety of traditional, non-intensive methods. This can only be achieved by coordinated planning of conservation measures among sites.     

Urban densification causes the decline of ground-dwelling arthropods

Urban densification is often considered has a green planning policy. However, its effects on woodland arthropods have been rarely analysed. To fill this gap, a multi-taxa approach using three ground-dwelling arthropod assemblages was conducted on 11 woodlands located along an urbanisation gradient. The gradient range from rural areas to one of the most urbanized cities in the world: Paris (France). Spiders, ground beetles and rove beetles were sampled with pitfall traps. We addressed the two following questions: (i) do the responses to urbanisation differ between taxa and/or between trait groups (habitat affinity to woodlands and dispersal capability) along the gradient? (ii) do the richness and abundance show a linear or an intermediate response? Our results showed a replacement of forest and non-flying species by generalist species and flying species with an increasing level of urbanisation. In term of species richness and abundance, the response varied between taxonomical and also trait groups. Some groups showed a strong linear decrease like forest carabids but other groups like spiders showed maximum values at intermediate levels of urbanisation. However, after a threshold of 70 % of built-in area, urbanisation negatively affected the species richness of all taxa and almost all trait groups, with a stronger effect on forest species. We suggest that the urban densification strongly impacted the assemblages of ground-dwelling arthropods by modifying both landscape and local properties of woodlands. To be considered as a green planning policy, the deleterious effects of urban densification should be mitigated.     

Hedgerows support rich communities of harvestmen (Opiliones) in upland agricultural landscape

Hedgerows play important roles in agricultural landscapes and they increase biodiversity by providing habitat refugia for species sensitive to agricultural disturbance. We have studied the characteristics of the communities of harvestmen (Opiliones) inhabiting hedgerows. Harvestmen are terrestrial arachnids associated with soil surface and subsurface and sensitive to land-use and disturbance. We were specifically interested in quantifying how hedgerow characteristics (e.g., elevation, length, width, connectivity, and plant diversity) affect harvestman diversity and community composition. We expected harvestman diversity and community composition to be positively related to both hedgerow size (area, length, width) and biological attributes of hedgerows (e.g., connectivity, plant community diversity). We surveyed hedgerow characteristics and harvestman communities of 20 hedgerows in an upland agricultural landscape in the Western Carpathians. Hedgerow characteristics were measured in the field or derived from GIS layers and we used correlation and ordination methods to relate them to harvestman community metrics. We found surprisingly high taxonomic richness of harvestmen within the studied hedgerows (15 species). Importantly, the Shannon index of harvestman communities was positively related to hedgerow length and hedgerow tree layer species richness and diversity. Harvestman community composition varied with hedgerow area and width. Despite their small total area, hedgerows represented an important habitat for diverse harvestman communities and hedgerow attributes such as size and tree diversity significantly affected the composition and the Shannon index of harvestman communities. Thus, greater lengths and widths of hedgerows can provide habitats for a higher Shannon index of harvestman communities, within surrounding agricultural landscapes.     

人工固沙植被恢复对地表节肢动物群落组成及多样性的影响

人工绿洲是干旱区主要的自然景观之一,为了维护绿洲稳定而营建的防护林强烈改变地表生态水文过程,进而影响着地上和地下生物多样性。然而,以往的研究对地上植被关注较多,而对土壤动物研究较少。以张掖绿洲外围人工固沙植被群落和天然固沙植被群落为研究对象,探讨人工固沙植被恢复对荒漠地表节肢动物群落组成及多样性的影响及不同动物类群对植被变化的响应模式。研究表明,天然固沙植被群落转变为人工固沙植被群落显著降低了地表节肢动物数量,但提高了地表节肢动物类群丰富度和多样性,这在5月份表现尤为明显。植被类型对地表节肢动物群落的影响不同,8月人工柽柳林群落地表节肢动物活动密度、类群丰富度和多样性均显著高于人工梭梭林群落。人工固沙植被恢复显著降低了适应荒漠环境的拟步甲科甲虫,而蚁科和部分蜘蛛的数量显著增加,它们对人工固沙植被恢复的响应模式不同决定了群落结构及多样性的变化规律。此外,研究还发现一些地表节肢动物类群对不同生境具有强烈的指示作用,如拟步甲科等可指示荒漠生境,潮虫科等可指示梭梭林生境,而蠼螋科和狼蛛科等可指示柽柳林生境。综上所述,人工栽植固沙灌木形成的固沙植被群落导致了一些适应荒漠环境的地表节肢动物类群的数量降低,但也为更多的地表节肢动物类群提供了适应栖居环境和充足的食物资源等,从而提高了地表节肢动物的多样性。     

Broad‐scale patterns in plant diversity vary between land uses in a variegated temperate Australian agricultural landscape

Plant diversity is threatened in many agricultural landscapes. Our understanding of patterns of plant diversity in these landscapes is mainly based on small‐scale (<1000 m²) observations of species richness. However, such observations are insufficient for detecting the spatial heterogeneity of vegetation composition. In a case‐study farm on the North‐West Slopes of New South Wales, Australia, we observed species richness at four scales (quadrat, patch, land use and landscape) across five land uses (grazed and ungrazed woodlands, native pastures, roadsides and crops). We applied two landscape ecological models to assess the contribution of these land uses to landscape species richness: (i) additive partitioning of diversity at multiple spatial scales, and (ii) a measure of habitat specificity – the effective number of species that a patch contributes to landscape species richness. Native pastures had less variation between patches than grazed and ungrazed woodlands, and hence were less species‐rich at the landscape scale, despite having similar richness to woodlands at the quadrat and patch scale. Habitat specificity was significantly higher for ungrazed woodland patches than all other land uses. Our results showed that in this landscape, ungrazed woodland patches had a higher contribution than the grazed land uses to landscape species richness. These results have implications for the conservation management of this landscape, and highlighted the need for greater consensus on the influence of different land uses on landscape patterns of plant diversity.