新疆准噶尔盆地东部波斑鸨炫耀栖息地选择

2000年4－7月,通过野餐直接观察采样的方法,对准噶尔盆地东部波斑鸨炫耀栖息地进行了研究。结果表明：条块状高灌丛随机散布在视野开阔、地势平坦的小半灌木群落中是波斑鸨炫耀栖息地的景观特征;影响波斑鸨炫耀栖息地选择的主要环境因子是植物种数、植被盖度、密度和蹁高灌丛距离;炫耀地内的植物种数、植被盖度、植被密度和草本植物种数显著低于对照样方内的相应成分;绝大多数炫耀地位于低矮稀疏的半灌木群落中,同时又总是靠近条块状高灌丛。这种灌嵌景观的炫耀地植物群落结构为波斑鸨的生存、炫耀提供了理想场所。     

江苏盐城保护区獐的栖息地选择

1999年3月至2000年9月期间在江苏盐城保护区对獐的栖息地选择进行了研究。共记录了123个栖息地利用样方和300个任意样方,在样方中测定了5种生态因子(植被类型、植被高度、植被覆盖度、距水源距离和人为干扰距离)。不同季节獐对植被类型、植被高度和距水源距离的利用有显著差异,对植被覆盖度和人为干扰距离的利用有极显著差异。春季獐偏好选择白茅草滩、大穗结缕草滩、芦苇地和獐毛草滩;夏季主要选择碱蓬地、芦苇地和盐蒿草甸;秋季倾向于选择獐毛草滩、盐蒿草甸、藨草滩和大米草滩。在春、夏、秋季,獐都倾向于选择高度在90-110cm的植被。在不同季节獐都偏好选择植被覆盖度>90%的栖息地,主要选择距离水源200-599m之间的栖息地。     

江苏大丰麋鹿自然保护区栖息地退化特征

通过对大丰麋鹿保护区栖息地植物群落特征的调查分析,揭示麋鹿栖息地退化机理.结果表明:围栏内、外草地群落相似性系数低,围栏内植物群落中地上部生物量、物种数、丰富度指数、Shannon指数、均匀度指数均低于围栏外草地,但生态优势度指数高于围栏外草地;其次,围栏内草地植物群落之间距离越远,群落相似性系数则越低;围栏内狼尾草种群的物种优势度均占绝对优势,但随着距离麋鹿活动中心渐远,群落均匀度指数呈上升趋势,狼尾草生物量占群落总生物量的比例、狼尾草种群特征值则均呈下降趋势.综合分析认为,火烧灭蜱可能是形成麋鹿栖息地植被现状的主要原因,研究结果为大丰麋鹿保护区栖息地的生态恢复提供理论依据.     

黑叶猴对广西扶绥破碎生境的选择和利用

从2001年3月至12月,对生活在广西扶绥珍贵动物保护区内-孤立石山上的一群黑叶猴(Trachypithecus francoisi)进行观察.通过收集有关栖息地利用的数据,探讨栖息地的破碎化对黑叶猴生态习性的影响.为分析人类活动对柄息地植被的影响,作者设置了10个植被样方,其中5个位于人类活动频繁的山坡;5个位于人类活动较少的山顶.观察结果表明,山坡的植物种类、多样性以及植物密度均低于山顶;山顶上黑叶猴喜食植物的密度也明显高于山坡.扶绥黑叶猴生境喜好程度分析表明,猴群偏好在食物丰富而人类活动少的山顶休息和觅食,而很少利用人类活动频繁的山坡.雨季里,猴群明显增加对山顶的利用率,而相应地减少对崖壁的利用.因此,扶绥黑叶猴对栖息地选择和利用可能是觅食利益和躲避人类活动干扰权衡的结果.黑叶猴选择崖壁上的突出平台或石洞作为夜宿地;通常重复利用少数几个夜宿地,并且会连续利用同一个夜宿地.     

野生扬子鳄栖息地植被多样性

2003年6～7月,采用样方法,对野生扬子鳄在安徽省南陵县、泾县、广德县、郎溪县和宣城地区等5县市的22个栖息地的植被进行了野外实地调查,并对植物种类作了详细的记录和分析,结果发现,野生扬子鳄栖息地植被均属于次生性植被,共有维管束植物92科294种;苦竹(Pteioblastus amarus)灌丛广泛分布于每个栖息地;22个调查点的植被多样性存在一定的差异．同时还初步分析了野生扬子鳄与栖息地植被多样性之间的关系,为野生扬子鳄的保护提供植物生态学基础资料。     

高原鼢鼠食性的研究

在高寒草甸和高寒灌丛两种栖息地中捕获高原鼢鼠 1 44只 ,将 92只鼢鼠的胃内容物对照已知植物组织的显微结构进行分析 ,以确定其食物组成。研究结果表明 ,虽然两种栖息地之间的植被组成有极大的差异 ,但是高原鼢鼠的食物组成在两种栖息地之间和性别之间均无明显的不同 ,不同植物出现的频次却有明显的差异。禾本科植物在高原鼢鼠的胃内容物中基本没有发现 ,对莎草科植物也只取食两个物种 ,高原鼢鼠所取食的植物主要是杂类草。在两种栖息地中高原鼢鼠喜食度指数最高的 9种植物均为鹅绒委陵菜、直立梗唐松草、丽江风毛菊、雪白委陵菜、美丽风毛菊、细叶亚菊、异叶米口袋、磨岭草和棘豆。     

栖息地荒漠化对蜥蜴群落组成的影响

栖息地改变往往对动物群落及其物种多样性有重要影响,但是目前关于栖息地荒漠化如何影响蜥蜴的群落组成鲜有研究。在内蒙古自治区鄂尔多斯市准格尔旗和达拉特旗地区通过样线法调查了三类不同荒漠化程度样地上的蜥蜴群落组成差异,用典范对应分析探究了关键的影响因素。结果表明,栖息地荒漠化使蜥蜴的群落组成发生显著变化,从固定沙丘、半固定沙丘到流动沙丘,草原沙蜥均是蜥蜴群落的优势物种,密点麻蜥逐渐减少,丽斑麻蜥则消失于荒漠化严重的半固定沙丘和流动沙丘中。随栖息地荒漠化程度的增加,蜥蜴的数量显著减少,密度显著降低,蜥蜴物种的丰富度、香农-威纳(Shannon-Weaver)多样性指数和皮洛(Pielou)均匀性指数均逐次显著下降,而辛普森(Simpson)优势度指数则逐次显著升高。这说明荒漠化不仅使蜥蜴群落组成变得简单,同时造成了蜥蜴物种多样性的下降甚至丧失。荒漠化也使蜥蜴的栖息条件发生显著变化。植被高度、油蒿比例、裸地比例、隐蔽度、表层土壤含水量和表层土壤孔隙度在三类栖息样地之间均存在极显著差异。典范对应分析结果表明,这些环境因子与蜥蜴群落组成的变化密切相关。总体而言,草原沙蜥偏好裸地,密点麻蜥偏好隐蔽性好且土壤湿润又疏松的区域,而丽斑麻蜥则偏好植被高的区域。     

基于栖息地斑块尺度的青弋江河源溪流鱼类群落的时空格局

确定鱼类的栖息地利用格局是研究物种与环境关系的基础, 也是鱼类多样性保护和管理的必要前提。目前, 有关溪流鱼类群落的栖息地斑块利用格局尚存在争议。基于2012年9月至2013年8月对青弋江河源溪流的逐月调查数据, 初步研究了鱼类群落的栖息地斑块利用格局, 着重在栖息地斑块尺度上解析了鱼类群落的时空变化规律。主要研究结果显示, 深潭和急滩2类斑块间的底质、流速、水深、溶氧栖息地因子显著差异, 且深潭斑块的环境稳定性高于急滩。研究共采集鱼类15种, 其中鲤科鱼类8种, 占采集物种数50%以上。基于鱼类物种存在与否的不连续变量的分析结果显示, 鱼类物种组成的斑块间和月份间变化均不具显著性。但是, 基于鱼类物种多度的连续变量的分析结果显示, 鱼类群落结构存在有显著的斑块间变化和时间动态; 就斑块间变化而言, 原缨口鳅(Vanmanenia stenosoma)在急滩斑块中的多度更高, 而宽鳍 (Zacco platypus)、光唇鱼(Acrossocheilus fasciatus)和尖头 (Phoxinus oxycephalus)等其他关键物种则在深潭中具有更高多度。深潭斑块的鱼类物种数显著高于急滩, 但2类斑块间的个体数无显著差异。深潭斑块的鱼类物种数较稳定, 而个体数月变化显著, 可能与鱼类繁殖和群体补充以及越冬死亡等有关; 急滩鱼类物种数和个体数的月变化均显著, 除了与鱼类群体补充和越冬死亡有关以外, 还可能受越冬时栖息地斑块选择变化的影响。上述结果表明, 在栖息地斑块空间尺度上, 由于研究区域内大多数物种在栖息地斑块选择上无明显的特化性, 深潭和急滩斑块间鱼类的物种组成分布不符合前人所报道的生境-共位群格局, 但区域内常见种多度的变化可引起鱼类群落结构的斑块间差异和季节动态。       

近丘间低地沙障促进沙丘植被恢复的效应

流动沙丘区的丘间低地的土壤种子库大,种类丰富,但其对流动沙丘植被恢复的作用尚不清楚.以科尔沁沙地为研究对象,在靠近丘间低地的下风向裸沙段设置沙障,研究了其对土壤种子库、幼苗出土与植物定居的效应.结果表明:沙障处土壤种子库物种数和密度都显著大于对照处(P<0.05),5-10 cm深度种子密度达到土壤种子库密度的60%,而对照处低于50%;沙障内的沙生植物出土和定居幼苗密度都显著大干对照处(P<0.001),沙障处与对照处的非沙生植物出土幼苗密度低于1株·m~(-2),建植幼苗密度低至0.1株·m~(-2);对照处种子数与幼苗出土和定居的相关性相对于沙障处的更强,沙生植物种子数与幼苗出土和定居的相关性相对于非沙生植物的更强;对照处种子库与幼苗出土和定居的物种组成相似性较沙障处大,沙生植物种子库与幼苗出土和定居的相似性较非沙生植物大.可见,沙障截留来自丘间低地的种子增加了流动沙丘的土壤种子库种类和密度,改变了土壤种子库的空间格局;沙障的设立提高了沙生植物幼苗的出土和物种定居的水平,但没有显著提高非沙生植物幼苗的萌发和建植.     

红腹锦鸡的冬季栖息地

采用样方法研究了红腹锦鸡冬季栖息地的地理特征、植被组成等特点。结果表明：红腹锦鸡对栖息地的坡度具有明显的选择性,而对坡向的选择性则不明显。栖息地植被层次明显,其中乔木层主要决定着栖息地植被的外貌和内部环境;灌木层对红腹锦鸡的活动有较大影响。灌木植物火棘的果实较多地被红腹锦鸡所取食。     

Plant functional group composition and large‐scale species richness in European agricultural landscapes

Question: Which are the plant functional groups responding most clearly to agricultural disturbances? Which are the relative roles of habitat availability, landscape configuration and agricultural land use intensity in affecting the functional composition and diversity of vascular plants in agricultural landscapes? Location: 25 agricultural landscape areas in seven European countries. Methods: We examined the plant species richness and abundance in 4 km × 4 km landscape study sites. The plant functional group classification was derived from the BIOLFLOR database. Factorial decomposition of functional groups was applied. Results: Natural habitat availability and low land use intensity supported the abundance and richness of perennials, sedges, pteridophytes and high nature quality indicator species. The abundance of clonal species, C and S strategists was also correlated with habitat area. An increasing density of field edges explained a decrease in richness of high nature quality species and an increase in richness of annual graminoids. Intensive agriculture enhanced the richness of annuals and low nature quality species. Conclusions: Habitat patch availability and habitat quality are the main drivers of functional group composition and plant species richness in European agricultural landscapes. Linear elements do not compensate for the loss of habitats, as they mostly support disturbance tolerant generalist species. In order to conserve vascular plant species diversity in agricultural landscapes, the protection and enlargement of existing patches of (semi‐) natural habitats appears to be more effective than relying on the rescue effect of linear elements. This should be done in combination with appropriate agricultural management techniques to limit the effect of agrochemicals to the fields.     

Assessing the role of invasive weeds in the impact of successional habitats on the bird assemblage in overgrowing agriculture

Agricultural habitats are assumed to be biodiversity refuges. However, some studies treat agricultural land management as a cause of the biodiversity decline, to which habitat loss and heterogeneity may contribute. Between the crops, the successional habitats appear – ruderal plant communities and bush areas. Their influence on farmland biodiversity is unknown. This research assessed the impact of spatial relationships between agricultural areas, semi-natural meadows and successional habitats on the bird species richness, Shannon diversity index, and Faith’s phylogenetic diversity index. An additional habitat variable was the presence of weeds, i.e., invasive Caucasian hogweeds Heracleum sp., treated as crops in the past. The birds and habitats research was on 74 sites set in pairs (invaded vs control) in south-eastern Poland. Results showed that birds assembling in agricultural and semi-natural areas were more diverse and contained protected farmland species, while birds appearing in overgrown habitats (i.e., successional and invaded) were clumped with their habitat requirements. In the presence of plant invaders, ruderal habitats negatively affected the bird phylogenetic diversity index. In invaded sites, bush areas had no positive effects on the Shannon diversity index and species richness of birds, in contrast with control sites. The presented research suggests the need to re-evaluate the importance of successional non-crop habitats considered positive in agricultural landscapes if those habitats develop in areas with plant invasion.     

Assessing habitat and resource availability for an endangered desert bird species in eastern Morocco: the Houbara Bustard

In Morocco we tested the consistency between an a priori habitat classification based on topography, hydrology, vegetation structure and composition, and an a posteriori classification based on arthropod assemblages, in a plain supporting wild endangered Houbara Bustards. According to vegetation structure, we defined seven a priori habitats that differed significantly in perennial cover and height. A multivariate multiple regression analysis showed a significant relationship between arthropod assemblages and vegetation structure. Canonical Analyses of Principal Coordinates, conducted simultaneously on direct searches of arthropods and trapping data, showed significant differences between assemblages in both cases, and produced two similar constrained ordinations of six a posteriori habitats: esparto grass (Stipa tenacissima), temporarily flooded areas, fields, “reg” with short perennials, “reg” with tall perennials and wadis. The two sampling methods reflected a dominance of ants and beetles. Arthropod biomasses increased significantly in spring and then decreased significantly in summer for beetles, and in autumn for ants. No strong differences appeared between habitats within seasons, especially in spring, indicating a uniform distribution of food resources during the Houbara breeding season. The “reg” with short perennials had the highest ant biomass in summer. This “reg” and fields also supported the highest arthropod biomass in autumn. Variation in arthropod biomass was a pertinent factor that should be integrated into Houbara habitat selection studies. The definition of habitat availability based on easily identifiable landscape units, combined with empirical tests on arthropod communities provided an accurate classification for habitat selection studies and conservation planning.     

The diversity of insectivorous bat assemblages among habitats within a subtropical urban landscape

We investigated the bat (Microchiroptera) diversity of four major habitat types within a large Australian subtropical city (Brisbane, Australia) to determine whether species richness was affected by habitat changes associated with urbanization, as suggested from studies elsewhere. Forty sites, ten in each habitat type (remnant bushland, parkland, low‐density residential and high‐density residential) were surveyed using acoustic bat detectors on six non‐consecutive occasions. Fourteen bat species were recorded. The species accumulation curve of the entire Brisbane bat assemblage reached a plateau at 14 species. The total numbers of species in bushland, parkland, low‐density residential and high‐density residential habitats were 14, 13, 14 and 11 species, respectively. Asymptotic estimates of species richness for each habitat were close or equal to these totals. Mean asymptotic estimated species richness differed significantly among habitats, being lowest in high‐density residential sites and highest in low‐density residential sites. Evenness profiles were similar across habitats, and were not strongly dominated by a few species. Partitioning of diversity components showed that landscape (γ) diversity was mainly determined by the high species richness of low‐density residential and bushland habitats (α diversity), rather than high beta (β) diversity among habitats. These findings contradict those of other studies on bat diversity in which species richness was highest within ‘natural’ areas of the urban landscape and assemblages were dominated by one or two species. This highlights the need for caution in making generalizations based on existing information, which is dominated by studies in temperate regions.     

How does shoreline development impact the recruitment patterns of coral reef fish juveniles (Moorea Island,French Polynesia)?

The study examined the effects of coastal embankment building on fish recruitment in three habitat types (beach-rock, white sand and muddy sand) in the near shore and fringing reef habitats of Moorea lagoon (French Polynesia). The results showed a positive relationship between the presence of embankments and the density and species richness of juvenile fish along the shoreline (whatever the habitat types). However, embankments deteriorated adjacent fringing reefs (decrease of live coral), which led to a decrease of fish density on beach-rock and white sand sites, and a decrease of fish species richness on muddy sand sites.     

Seasonal changes in habitat use by Houbara Bustards Chlamydotis [undulata] macqueenii in northern Saudi Arabia

Habitat preferences by Houbara Bustards Chlamydotis [undulata] macqueenii in Harrat al-Harrah reserve, in northern Saudi Arabia were determined from sightings of birds in all seasons over three years. Vegetation and crawling invertebrate abundance were sampled in each habitat. Houbara Bustards showed seasonally changing habitat preferences that appeared to be influenced primarily by vegetation phenology, abundance and cover. More densely vegetated areas (10–17% cover) were preferred. Seasonal and inter-habitat variations in invertebrate numbers were not reflected in differential habitat use by Houbara Bustards. The highest selection ratio for a single habitat (dry lakes) occurred in summer, coinciding with the fruiting of Shafallah Capparis spinosa. Selectivity of habitats was least in spring, when green vegetation was most widespread. Changes in Houbara Bustard habitat preferences in response to marked seasonal changes in habitats brought about by well-defined patterns of rainfall indicate that studies of habitat selection should consider the entire annual cycle. The importance of vegetative cover and the sensitivity of Houbara Bustards to human disturbance suggest that reserves set aside for Houbara Bustards should be extensive, diverse and largely free of livestock, human occupation and its associated disturbances.     

Scale-specific correlations between habitat heterogeneity and soil fauna diversity along a landscape structure gradient

Habitat heterogeneity contributes to the maintenance of diversity, but the extent that landscape-scale rather than local-scale heterogeneity influences the diversity of soil invertebrates—species with small range sizes—is less clear. Using a Scottish habitat heterogeneity gradient we correlated Collembola and lumbricid worm species richness and abundance with different elements (forest cover, habitat richness and patchiness) and qualities (plant species richness, soil variables) of habitat heterogeneity, at landscape (1 km²) and local (up to 200 m²) scales. Soil fauna assemblages showed considerable turnover in species composition along this habitat heterogeneity gradient. Soil fauna species richness and turnover was greatest in landscapes that were a mosaic of habitats. Soil fauna diversity was hump-shaped along a gradient of forest cover, peaking where there was a mixture of forest and open habitats in the landscape. Landscape-scale habitat richness was positively correlated with lumbricid diversity, while Collembola and lumbricid abundances were negatively and positively related to landscape spatial patchiness. Furthermore, soil fauna diversity was positively correlated with plant diversity, which in turn peaked in the sites that were a mosaic of forest and open habitat patches. There was less evidence that local-scale habitat variables (habitat richness, tree cover, plant species richness, litter cover, soil pH, depth of organic horizon) affected soil fauna diversity: Collembola diversity was independent of all these measures, while lumbricid diversity positively and negatively correlated with vascular plant species richness and tree canopy density. Landscape-scale habitat heterogeneity affects soil diversity regardless of taxon, while the influence of habitat heterogeneity at local scales is dependent on taxon identity, and hence ecological traits, e.g. body size. Landscape-scale habitat heterogeneity by providing different niches and refuges, together with passive dispersal and population patch dynamics, positively contributes to soil faunal diversity. Electronic supplementary material The online version of this article (doi:) contains supplementary material, which is available to authorized users.     

冬季清凉峰山区小麂和野猪的生境选择及差异

从2005 年11 月5 日至2006 年1 月21 日,为了评估小麂和野猪的生境选择及其差异,我们在浙江清凉峰国家级自然保护区核心区共设置了248 个样方群。研究发现,两者都选择平缓坡的灌丛植被、草本密度小、离住宅较近和离隐蔽物距离适中的生境,表现了它们的生境选择有一定的重叠性。但是它们也表现出生境选择的一些差异,小麂选择乔木密度适中、灌丛密度大和郁闭度适中的生境,而野猪选择乔木密度小的生境,随机地使用各类灌丛密度和郁闭度的生境。小麂还选择北坡、离水源距离较远的生境,野猪只是随机地使用不同的坡向和离水源距离的生境。分析两者共存的机制,我们发现小麂采取隐藏策略而野猪采取逃跑策略来避敌和利用资源,即它们之间存在与反捕食策略相关的生境选择差异。