岛屿栖息地鸟类群落的丰富度及其影响因子

1997年1月至1997年12月间,以杭州市的园林鸟类群落为研究对象,对岛屿栖息地鸟类群落的丰富度与面积,人为干扰,内部结构和周围景观结构等多种因素的关系进行了系统的分析和检验。在杭州市各园林中共观察到82种鸟类。园林单次调查的鸟类物种数（S）与园林全年总物种数（Sy)与园林面积（A）的最佳回归拟合方程分别为;S＝ 2.7432A^0.3846,Sy=10.6574A^0.3669。杭州市园林鸟类群落物种－面积关系的成因不支持平衡假说,随机取样假说,栖息地多样性假说和干扰假说,岛屿栖息地鸟类群落的丰富度是多因素综合作用的结果,包括取样面积效应（排除了取样面积效应之后,小园林具有更高的物种密度）,栖息地结构的多样性（其中树种多样性是最主要的影响因子）,干扰因素,物种因素和研究尺度等几个方面。     

园林鸟类群落的岛屿性格局

岛屿群落由于受岛屿栖息地特征结构的影响而产生一系列特殊的格局。通过对杭州市园林鸟类群落的研究,分析了园林鸟类群落的物种数、组成和多度与园林岛屿性状的关系,从而确定了园林鸟类群落存在如下与园林的岛屿性状有关的格局:(1)在物种数方面,在相同的取样面积下,园林的物种数随园林面积的增大而减少;(2 )在群落组成上,园林鸟类群落呈现出不完全的嵌套格局,分布于物种数较少的园林中的物种多数也分布在物种数较多的园林中;(3)在物种多度方面,园林鸟类的总密度随面积的增大而减少,园林鸟类多度的均匀度随着面积的增大而提高。群落的岛屿性格局反映了栖息地的岛屿化对群落的影响,总称之为群落的岛屿效应。通过比较全年、繁殖季节、越冬季节和迁徙季节群落岛屿性格局的显著性,分析群落的稳定性与群落岛屿效应之间的关系,认为两者之间没有必然的联系,相对非稳定的群落也可导致显著岛屿效应     

中国大陆鸟类栖息地选择研究十年

栖息地选择研究一直是鸟类生态学研究的重要内容之一。通过对2001年1月至2010年12月10年期间中国大陆鸟类学家在国内外期刊上发表的鸟类栖息地选择研究的论文进行分析,对我国鸟类栖息地选择研究提出展望。10年间,我国鸟类学家共发表有关鸟类栖息地选择或利用的论文170篇,共涉及到鸟类10目31科73种。在这10年里,中国大陆有关鸟类栖息地选择或利用的文章持续增长。然而,我国鸟类栖息地选择的研究也存在着如下问题:(1)存在栖息地选择和栖息地利用误用的现象,这种现象在10年内并无明显改善;(2)在选择研究方法时,很少考虑个体的可获得性、种群密度及抽样尺度对栖息地选择的影响;(3)大多数的栖息地选择的论文没有对鸟类的栖息地选择行为进行研究,也缺乏对其选择的适合度背景去进行研究。根据这些问题,对我国未来的鸟类栖息地选择研究提出了建议。     

鸟类栖息地片段化研究的现状

栖息地片段化的形成及其影响的研究是鸟类生态学的研究热点之一。对鸟类栖息地片段化的研究内容进行了分类,阐述了存在的问题,展望了今后鸟类栖息地片段化研究与问题。     

鸟类栖息地片段化研究的理论基础

栖息地片段化是导致许多森林鸟类种群下降的主要原因之一,而对栖息地片段化的形成及其影响的研究已是成为鸟类生态学的研究热点之一。介绍了鸟类栖息地片段化研究的理论基础,即岛屿生物地理学理论、景观生态学理论以及集合种群理论等,并阐述了鸟类栖息地片段化研究范式转变的原因。     

栖息地破碎化与鸟类生存

栖息地破碎化给野生动物带来的不良后果是全球生态学家和保护生物学家共同关心的问题.自从提出栖息地破碎化是导致生物多样性丧失的关键因素之一的论点后,近20年来,栖息地破碎化研究一直是生态学和保护生物学最活跃的前沿研究领域之一.栖息地破碎化是一动态过程,可在多尺度上发生并蕴涵着复杂的空间模式变化.栖息地破碎化对鸟类的生态学效应主要体现在面积效应、隔离效应和边缘效应等.这些效应影响着鸟类的分布、基因交流、种群动态、扩散行为、种间关系和生活史特征等,最终影响着鸟类的生存.介绍和总结了栖息地破碎化过程、研究的理论依据及栖息地破碎化对鸟类生存产生的诸多影响.     

雪雀属鸟类栖息地在中国的分布

雪雀属（Montifringilla)属典型的高原鸟类,主要分布于我国青藏高原及其毗邻地区。本文依据现有雪雀属种类的采集记录、文献记载的分布资料,结合野外实地考察,运用GIS（地理信息系统）的叠加和分析功能,综合生境类型资料,建立其野生动物－栖息地关系模型,并预测该属种类栖息地分布。该模型依据适宜于雪雀分布的植被类型和高度叠加后产生雪雀的适宜栖息地,与县界的行政区划图叠加后产生预测有可能分布的县级单元。预测产生的分布图包含高度适宜、适宜和不适宜三种生境类型。本研究预测雪雀属种类的栖息地分布图显示,青藏高原大部分缺乏采集记录的地区具有适宜于雪雀分布的生境类型,具有雪雀分布所必须的潜在条件。而那些有采集记录的县,也仅仅在那些适宜的生境类型中才会有雪雀的分布。     

城市鸟类群落生态学研究展望

城市鸟类群落生态学是一个重要的但未引起足够重视的研究领域。城市化的后果和城市栖息地的特征已引起了部分生态学家的关注,同时也决定了它在研究内容和方法上的特殊性。城市化对野生动物的泛化影响以及城市鸟类群落生态学研究的潜在理论价值应该引起足够的重视。本文在总结国内外城市鸟类群落生态学研究现状的基础上,重点论述和探讨了目前的研究热点和今后的发展趋势,介绍了一些国外新的理论和方法在此领域研究上的应用状况,这     

乌鲁木齐市园林春秋季鸟类群落多样性

2011年4～5月、10～11月,用样线法对乌鲁木齐市中心城区5个园林鸟类群落的组成和多样性进行了调查,共记录到鸟类47种,隶属于9目23科,分布型以古北界为主。其中留鸟、夏候鸟和冬候鸟分别占鸟类总种数的44.68%、34.04%和10.64%,鸟类群落优势种为[树]麻雀Passer montanus、家麻雀Passer domesticus和乌鸫Turdus merula。园林鸟类的平均密度为(11.27±4.3)只/hm2(±S.D.),春季鸟类密度高于秋季,但二者差异不显著(F=0.002,P=0.194)。春季鸟类群落拥有较高物种丰富度和多样性,夏候鸟是此时鸟类群落的重要组成部分;秋季鸟类群落的多样性低而优势度较高,冬候鸟对群落结构影响不大。各园林样地记录到的鸟类种数和密度差异较为明显,园林的内部生境多样性与鸟类种数呈正相关(R=0.9,P=0.037)。     

澳门城市栖息地斑块中鸟类群落功能和谱系多样性

了解群落构建过程是生态学的核心和基本问题,这对于解释物种共存和物种多样性的维持,完善生物多样性保护政策至关重要。与传统的物种多样性相比,功能和谱系多样性能够提供更多的信息,特别是在群落构建过程方面提供深刻见解。2014年5月—2017年1月,采用样线法对澳门地区5个城市栖息地斑块中(生态一区、鹭鸟林、赛马场滩涂、关闸口岸滩涂和莲花桥侧红树林)的鸟类进行繁殖季和越冬季的调查,共调查14次。利用鸟类丰富度和多度来表征群落的物种多样性,其中多度以最大值保留法计;功能和谱系多样性分别采用功能丰富度(functional richness:FRic)和Faith’PD。同时,利用基于多度加权的平均成对功能距离(mean pairwise functional distance,MFD)和平均成对谱系距离(mean pairwise phylogenetic distance,MPD)来表征群落的功能和谱系结构。结果表明:共记录98种鸟类,隶属于14目32科,目、科、种中数量最多的依次为,雀形目鸟类最多为47种,鹭科物种数为11种,白鹭多度为849只;鸟类物种丰富度(68种)和PD在生态一区最高,...     

上海城市绿地冬季鸟类群落特征与生境的关系

2005年11月至2006年2月对上海市区绿地鸟类进行了调查,共记录到鸟类34种,隶属5目16科。研究发现冬季鸟类群落结构相对稳定,优势种为麻雀(Passer montanus)和白头鹎(Pycnonotus sinensis)。冬季鸟类群落多样性受多种因素的影响,其中绿地面积、乔木盖度和栖息地类型多样性是影响鸟类多样性的关键因子。聚类结果表明,面积大、生境类型丰富及人为干扰相对较少的绿地,鸟类多样性高。因此提出如下建议:(1)增加城市中植物种类,特别是乡土物种,适当提高冬季常绿乔木以及乔、灌、草的比例;(2)在绿地中尽可能多地保留自然生境;(3)在城市绿地中适当开辟湿地生境,以吸引水鸟栖息。     

环境因子对上海城市园林春季鸟类群落结构特征的影响

2004年3—5月,对上海8个园林绿地的春季鸟类做了研究。在调查中共观察到55种鸟类,其中留鸟31种,候鸟24种。运用回归与相关统计分析方法分析了鸟类群落结构和分布特征与8个园林绿地的公园面积、水体比例、植被种数、乔木层盖度、灌木层盖度、草本层盖度、地形坡度异质性、临主干道状况、人流量、行道宽度10项环境指标的关系。结果表明：(1)公园面积、植被种数、灌木层盖度、草本层盖度、地形坡度异质性、临主干道状况、行道宽度等7个因子在影响园林鸟类群落结构和分布中起关键性作用;(2)上海城市鸟类数量、多样性呈单一化趋势,而且公园绿地内大面积水体等建设方案并不利于鸟类的栖息。     

Home range size of willow tits: a response to winter habitat loss

We examined the behavioral response to habitat loss and fragmentation of willow tits (Parus montanus) in winter in a mosaic forest landscape in northern Finland. We studied habitat preference, flock size and home range size of 16 flocks, half of which had their territories in forests fragmented by forestry and half in continuous forest. We predicted that birds would respond to habitat loss by enlarging their home range and/or diminishing group size. In addition, to compensate for fragmentation effects, willow tits might be expected to include more optimal habitat into their territories. Flocks included on average 3.9 birds and occupied territories of 12.6 ha. Willow tits avoided open areas (clear cuts and young sapling stands) and preferred mature forests and older sapling stands or pine bogs equally. Birds responded to habitat loss by enlarging their home ranges but not by reducing the group size. Large territories included a smaller proportion of mature forests, but the proportion of sapling and pine bog habitat did not change. Birds on territories that included a large proportion of open habitat localized their activity on several distinct habitat patches that were distributed over a wide area. We conclude that willow tits adjust territory use to compensate for the inclusion of unsuitable habitat within home ranges, and older sapling areas and pine bogs serve as surrogates for mature forests. However, birds did not enlarge the proportion of forest habitat in their territories with increasing habitat loss. Thus, our data do not suggest a strong effect of fragmentation, but imply that forestry practices reduce suitable wintering habitat and carrying capacity in the area. Thus winter habitat loss may explain the observed population decline of willow tits in Finland during recent decades.     

Financial Costs of Conserving Captive-bred Wild Birds

This communication presents and discusses the financial costs recorded by a small Brazilian aviary in which a few captive-bred wild bird species have been kept. The highest expenses were associated with the birds’ diet, accounting for at least 60% of total costs. Among insectivorous-frugivorous birds, this figure was 88%. The most expensive food item was live food. Although initial costs for enclosures may be considerable, their durability means expenditures can be spread over time, mitigating their impact. Approximately 30% of the total costs for keeping the largest species studied here were linked to a spacious outdoor planted aviary. Quail from this flock required additional sanitary expenditure (i.e. 14% of the total) for controlling a previous parasitic infection. Total annual maintenance costs amounted to USD 298.00, USD 211.00 and USD 116.00 for each Pekin robin (Leiothrix lutea Scopoli, 1786), Livingstone's turaco (Tauraco livingstonii Gray, 1864), and Valley quail (Callipepla californica Shaw, 1798), respectively.     

北京城市鸟类对食源植物利用规律

园林植物为城市生活的鸟类提供重要食物资源,园林中的植物配置会影响城市中鸟类的种类、数量和群落结构.研究城市鸟类与食源植物的关系,可明确鸟类对食源植物的取食关系,为提高城市鸟类多样性提供技术支撑.2017至2019年,在北京市范围内,以直接观察法和野外照片识别法记录鸟类取食的食源植物种类和数量.共选取6个研究地点,每个研...     

天津大黄堡湿地自然保护区鸟类调查

2005年3~12月,对天津武清区大黄堡自然保护区的鸟类资源进行了调查,共记录到鸟类17目47科199种,其中国家Ⅰ、Ⅱ级重点保护鸟类37种;水鸟92种,水鸟在种类和数量上都构成了本地区鸟类的主体。数量分析划分1 000只以上为优势种,有12种。依居留状况分析,旅鸟148种、夏候鸟55种、冬候鸟14种、留鸟14种。     

中度嗜盐或耐盐放线菌生长对阴离子选择性研究*

长期以来Cl^-被作为主要阴离子来分离和培养中度嗜盐放线菌,但是盐湖中还含有NO3^-、SO4^2-、CO3^2-和HCO3^-等阴离子。培养基中只加入含有Cl^-的盐,不能完全模拟出自然界的环境,因此对中度嗜盐或耐盐放线菌的研究会有一定的限制。实验通过研究部分中度嗜盐或耐盐放线菌菌株生长对阴离子的选择影响,结果发现中度嗜盐或耐盐放线菌对部分阴离子如NO3^-和SO4^2-没有太大的选择性,Cl^-可以被NO3^-和SO4^2-所代替;但有些阴离子如CO3^2-和HCO3^-仅对拟诺卡氏菌属(Nocardiopsis)影响较小,对盐碱环境中的其他属的放线菌,如普氏菌属(Prauserella)、链单孢菌属(Streptomonospora)、糖单孢菌属(Saccharomonospora)等影响较大。     

马粪海胆对环境变化的耐受性与选择性研究

对采自青岛近岸的马粪海胆进行温度、盐度、光强与底质等因子的耐受及选择实验。结果表明,青岛近岸马粪海胆的适温范围约在8-22℃,对温度的选择受驯养水温的影响;属窄盐性种类,适盐范围约在30-35;喜好弱光环境,饥饿状态的选择光强（8-25lx）较非饥饿状态（10-35lx）低;对粗沙砾底质具明显的正选择,而对细沙性底质呈明显的负选择。     

Avian diversity in a Kenyan agroecosystem: effects of habitat structure and proximity to forest

Tropical agroecosystems cover an increasingly large proportion of the Earth’s terrestrial surface. Yet, relatively little is known about the factors that influence their avifauna, especially in areas of high human population density. The potential of tropical farmland for sustaining bird biodiversity, including forest birds, can be influenced by habitat structure and the distance from the nearest forest. We investigated the effect of these two factors on the bird community in the farmland near Kakamega Forest, Kenya. Using point counts, we assessed the number of bird species and individuals on 56 study plots in distances up to about 2,100 m from the forest. We observed a total of 96 bird species in the farmland, 22 of which were forest, 58 shrub-land, and 16 open-country species. High vertical vegetation heterogeneity and a large number of woody plant individuals were related to high species richness of forest and shrub-land birds, whereas open-country birds avoided such areas. The species richness and total number of forest birds declined with increasing distance to the forest. A comparison with the bird community within Kakamega Forest indicated that only a fraction of the forest species could be sustained in the farmland. This suggests that agroecosystems with a diverse habitat structure can support a high diversity of birds, but have only a limited capacity to compensate for forest loss. Electronic supplementary material The online version of this article (doi:) contains supplementary material, which is available to authorized users.     

Viability of meta-populations of wetland birds in a fragmented landscape: testing the key-patch approach

The key patch approach assumes that metapopulations in fragmented landscapes are likely to be viable with at least one “key” sub-population that is sufficiently large to ensure re-colonization of surrounding minor habitat patches. It is based on a minimum viable number of breeding pairs and within-breeding season dispersal distance, linked to size of the animal and longevity. It was tested using census data of 15 wetland bird species (bearded tit, bluethroat, great reed warbler, sedge warbler, Savi’s warbler, grasshopper warbler, spotted crake, water rail, common snipe, common teal, garganey, little bittern, night heron, great bittern and marsh harrier) in 14 wetland complexes of variable size (3–55 km²) spread across the Netherlands (distances ranging 4–156 km). First, for each species it was assessed whether a wetland harbored a key subpopulation, which was the case for the sedge warbler (7 key subpopulations), grass-hopper warbler (2), water rail (2), bearded tit, bluethroat, Savi’s warbler, common teal, garganey, great bittern and marsh harrier (all one key subpopulation).Together with the adjacent sub-populations present within breeding season dispersal distance, 10 out of the 15 studied species formed viable meta-populations. This was compared with the trend in the census data of 13 species for 1990–2000 and was found to correspond significantly (likelihood ratio test, P = 0.003): species without a viable meta-population had declined (2 out of 4) or remained stable (2 out of 4), whereas viable meta-populations had increased (6 out of 9) or remained comparatively stable (2 out of 9). One wetland complex, the Oostvaardersplassen, stood out in that it haboured key sub-populations for 9 out of the 15 species studied. Variation in quantity of specific habitat (area or perimeter marshland, woodland or open water) in a wetland complex was of limited importance explaining abundance patterns, since all covaried strongly with total area among the wetland complexes, with the exception of water perimeter. Apparently, these wetlands on peat harbour largely similar landscapes. Indeed, population sizes of most birds covaried strongly and in a PCA two distinct clusters of species were identified that shared high numbers of breeding pairs in the same, larger, wetland complexes, the first (3 species) including the great reed warbler, and the second (9 species) the water rail.