四川扭角羚春冬季对栖息地的利用初步研究

1998年3月至1999年2月,在四川省青川县唐家河自然保护区,对四川扭角羚（Budorcas taxicolor tibetana)春冬季对栖息地的利用进行了初步研究。结果表明,影响四川扭角羚春季栖息地利用的主要生态因子为人为干扰,植被型、乔木大小、乔木距离,乔木密度、食物丰富度,海拔,坡位、郁闭度,影响冬季栖息地利用的主要生态因子为人为干扰。植被型,乔木距离,灌木大小,灌木密度,动物干扰度,乔木大小、灌木距离,坡位,郁闭度,水源,四川扭角羚春冬季栖息地利用的分离主要表现为食物丰富度,乔木大小,乔木密度,乔木距离,植被型,水源,坡位等生存因子的分离。     

How accurate are population models? Lessons from landscape‐scale tests in a fragmented system

There is a growing debate about the ability of Population Viability Analysis (PVA) to predict the risk of extinction. Previously, the debate has focused largely on models where spatial variation and species movement are ignored. We present a synthesis of the key results for an array of different species for which detailed tests of the accuracy of PVA models were completed. These models included spatial variation in habitat quality and the movement of individuals across a landscape. The models were good approximations for some species, but poor for others. Predictive ability was limited by complex processes typically overlooked in spatial population models, these being interactions between landscape structure and life history attributes. Accuracy of models could not be determined a priori, although model tests indicated how they might be improved. Importantly, model predictions were poor for some species that are among the best‐studied vertebrates in Australia. This indicated that although the availability of good life history data is a key part of PVA other factors also influence model accuracy. We were also able to draw broad conclusions about the sorts of populations and life history characteristics where model predictions are likely to be less accurate. Predictions of extinction risk are often essential for real‐world population management. Therefore, we believe that although PVA has been shown to be less than perfect, it remains a useful tool particularly in the absence of alternative approaches. Hence, tests of PVA models should be motivated by the cycle of testing and improvement.     

白冠长尾雉育雏期的栖息地选择

20 0 1年 4～ 8月 ,在河南省董寨国家级自然保护区对白冠长尾雉 (Syrmaticusreevesii)育雏期的栖息地进行了调查。野外共遇见 2 4个不同的家族群 ,平均大小为 (2 96± 0 35 )只。白冠长尾雉的家族群主要在针阔混交林中活动 ,这些地方的坡向以东南方向居多、坡度较缓而坡位靠下 ,与林缘的距离大于 6 0m而与水源的距离通常小于 30m。逐步判别分析的结果表明 ,与林缘的距离、乔木胸径、灌木盖度、草本植物的种类和高度等是影响白冠长尾雉家族群栖息地选择的关键因子 ;植被结构 ,尤其是草本植物的特征 ,是影响家族群栖息地选择的主要方面。建议在对白冠长尾雉采取保护措施时 ,从提供丰富的食物资源和良好的隐蔽条件入手。注意保护现存栖息地 ,在育雏期保护好草本植物。     

Climate change-integrated conservation strategies

Aim Conservation strategies currently include little consideration of climate change. Insights about the biotic impacts of climate change from biogeography and palaeoecology, therefore, have the potential to provide significant improvements in the effectiveness of conservation planning. We suggest a collaboration involving biogeography, ecology and applied conservation. The resulting Climate Change‐integrated Conservation Strategies (CCS) apply available tools to respond to the conservation challenges posed by climate change. Location The focus of this analysis is global, with special reference to high biodiversity areas vulnerable to climate change, particularly tropical montane settings. Methods Current tools from climatology, biogeography and ecology applicable to conservation planning in response to climate change are reviewed. Conservation challenges posed by climate change are summarized. CCS elements are elaborated that use available tools to respond to these challenges. Results Five elements of CCS are described: regional modelling; expanding protected areas; management of the matrix; regional coordination; and transfer of resources. Regional modelling uses regional climate models, biotic response models and sensitivity analysis to identify climate change impacts on biodiversity at a regional scale appropriate for conservation planning. Expansion of protected areas management and systems within the planning region are based on modelling results. Management of the matrix between protected areas provides continuity for processes and species range shifts outside of parks. Regional coordination of park and off‐park efforts allows harmonization of conservation goals across provincial and national boundaries. Finally, implementation of these CCS elements in the most biodiverse regions of the world will require technical and financial transfer of resources on a global scale. Main conclusions Collaboration across disciplines is necessary to plan conservation responses to climate change adequately. Biogeography and ecology provide insights into the effects of climate change on biodiversity that have not yet been fully integrated into conservation biology and applied conservation management. CCS provide a framework in which biogeographers, ecologists and conservation managers can collaborate to address this need. These planning exercises take place on a regional level, driven by regional climate models as well as general circulation models (GCMs), to ensure that regional climate drivers such as land use change and mesoscale topography are adequately represented. Sensitivity analysis can help address the substantial uncertainty inherent in projecting future climates and biodiversity response.     

Management and restoration of European eel population (Anguilla anguilla): An impossible bargain

The European eel panmicitic population has been declining at least since the 1980s throughout its distribution area. The stocks are now ten times lower than they were initially. The causes of this decline are reviewed in this paper: marine causes such as Gulf Stream shifts are thought to reduce survival of leptocephali larvae during their transoceanic migration, but inland causes are also suspected, i.e. overfishing of all continental stages, obstructions to upstream and downstream migrations, habitat loss, water quality, parasite and xenobiotic contamination, which together contribute to reducing quality and quantity of spawner escapement from European inland waters to sea. Restoration programs have been conducted in several inland hydrosystems in Europe. If local fisheries have been sustained mainly by stocking elvers and glass eels, no significant restoration of the population has been observed suggesting that restoration plans are inefficient, despite significant efforts and relevant technologies (fish passage). The causes for the failure of restoration projects are listed and discussed, and it is shown that the minimum scale to work at is the catchment area. But international cooperation is required to coordinate programs, to determine common objectives and policies. Concepts for sustainable restoration and management are provided and discussed together with the general interest of eel population as a biointegrator of the quality and integrity of inland hydrosystems.     

高黎贡山冬季白尾梢虹雉运动方式和生境偏好的初步观察

2002及2003年1月,两次对高黎贡山大脑子白尾梢虹雉(Lophophorus sclateri)的运动方式和活动痕迹做了直接观察或样带／样方取样。该鸟滑翔是下行的主要运动方式,上行全为行走;所发现的3个夜宿地均位于坡度大、郁闭度高的近沟谷地带;冬季向低海拔迁移,与降雪有关,使得近沟谷带成为密集利用带。这样的运动和生境利用方式,显然是能耗最小化和觅食效率最大化的行为适应。     

上海农耕区鸟类群落特征及与几种生境因子的关系

2000-2002年冬季和夏季,采用固定样带法在上海郊区所有区县选择了17条样带,对农耕区鸟类做了4次抽样调查。记录了鸟类的组成、数量、出现频率及生境因子特征。根据调查数据,计算鸟类密度、多样性、均匀度、优势度、生物量、相对重要值等群落特征参数。调查共记录到鸟类76种,隶属13目26科。平均密度为5．19只／hm^2,多样性指数为1．8742。优势种为麻雀、家燕、白头鹎、棕背伯劳和白鹊鸰。鸟类组成中水鸟(夜鹭、白鹭等)较多,占了总数的1／3;与上海其他区域相比,鸟类密度较高,但种类相对较少,数量集中在少数几个物种(麻雀、家燕、白头鹎、棕背伯劳等)。鸟类物种丰富度与荒地面积呈显著正相关,与环境污染程度呈显著负相关,与林地面积、人口密度、水体面积等相关不显著。提示荒地对鸟类多样性非常重要。     

How does Reynoutria invasion fit the various theories of invasibility?

Questions: 1. How does species richness of recipient communities affect Reynoutria invasion? 2. How does Reynoutria invasion change host community structure? 3. Are there any differences in habitat preferences among three closely related Reynoutria taxa? 4. How does the genetic structure of Reynoutria populations change along the course of a river? Location: River Jizera basin, north Bohemia, Czech Republic. Methods: Nine 0.25 km² plots were chosen along the river. Within each plot all main habitat types were determined and sampled using the Braun‐Blanquet scale to determine the invasibility of various communities. The patches invaded by Reynoutria taxa and surrounding Reynoutria‐free vegetation in the same habitat type were sampled as relevé pairs to compare the composition of invaded and non‐invaded vegetation. In addition, to characterize the genetic structure of Reynoutria populations along the river, 30 samples from different clones were collected. Results and conclusions: 1. The species richness of communities has no influence on the success of Reynoutria invasion in the area studied. The combination of environmental conditions and propagule spread is more important to the invasion success than the number of species in the host community. 2. Reynoutria invasion greatly reduces species diversity. 3. R. japonica invaded more habitat types than R. sachalinensis and R.×bohemica. The hybrid R.×bohemica outcompetes the parental taxa at sites where both taxa co‐occur. 4. Isozyme analysis revealed phenotype variability in the hybrid in contrast to the parental taxa. Different hybrid phenotypes are distributed randomly on the middle and lower reaches of the River Jizera; one of them dominates and the other three occur occasionally. This pattern supports the hypothesis that sexual reproduction occasionally occurs within Reynoutria taxa.     

Effects of environment,habitat configuration and forest continuity on the distribution of forest plant species

In present day European landscapes many forest plant species are restricted to isolated remnants of a formerly more or less continuous forest cover. The two major objectives of this study were (1) to determine the relative importance of habitat quality (mainly in terms of soil parameters), habitat configuration (patch size and isolation) and habitat continuity for the distribution of herbaceous forest plant species in a highly fragmented landscape and (2) to examine if groups of species with different habitat requirements are affected differently. Deciduous forest patches in northwestern Germany were surveyed for the presence of a large set of forest species. For each patch, habitat quality, configuration and continuity were determined. Data were analysed by Redundancy Analysis with variation partitioning for effects on total species composition and multivariate logistic regression for effects on individual species, for two different data sets (base‐rich and base‐poor forest patches). Overall, we found strong effects of habitat quality (particularly of soil pH, water content and topographic heterogeneity in the base‐rich forest patches; and of calcium content and disturbance in the base‐poor patches), but only relatively weak effects of habitat configuration and habitat continuity. However, a number of species were positively affected by patch area and negatively affected by patch isolation. Furthermore, the relative importance of habitat configuration tended to be higher for species predominantly growing in closed forests compared to species occurring both in the forest and in the open landscape.