红外相机技术在河北雾灵山国家级自然保护区中的应用

为了充实河北雾灵山自然保护区的野生动物资源本底资料,提高监测能力和监测水平,雾灵山保护区自2015年开始将红外相机技术应用到野生动植物的资源调查和管护中。目前应用红外相机技术发现兽类5目10科14种,鸟类4目6科10种,掌握了区内主要物种猪獾(Arctonyx collaris)、狍(Capreolus)和勺鸡(Pucrasia macrolopha)的日活动节律,补充了保护区的本底调查资料,为保护区进一步开展金钱豹(Panthera pardus)、斑羚(Naemorhedus goral)和鸟类多样性等科学研究奠定了基础,为保护区制定关于野生动物资源的相关管护政策提供了科学依据。     

武功山国家森林公园的自然生态化规划设计实践

森林是重要的自然资源，在开发方式上应十分慎重。以自然生态化规划设计思想作为指导思想，进行了武功山国家森林公园的规划和设计，进行了森林公园可持续规划设计的探索。     

健身与竞技

本文论述了健身与竞技及其联系、区别、宣传全民健身计划、奥运争光计划.重健身,提高人体素质,显示竟技水平,展示中华民族之神气,促进人类文明进步.     

双斜立式油缸木材抓具优化设计研究

通过对现行木材生产中所使用的双斜立式油缸木材抓具的受力情况的深入分析。推导了双斜立式油缸木材抓具在两种不同的工作状态下的抓取力计算公式。在此基础上,结合现代先进的设计方法——优化设计法的基本思想,建立了该类型木材抓具优化设计的数学模型。根据数学模型的特点,给出了能够处理约束优化问题的优化计算方法——内点惩罚函数法,编制了该方法的计算机程序,并对程序的使用进行了必要的说明。     

绵羊慢病毒自然感染绵羊的硬化性淋巴细胞性乳腺炎

７头来自新疆南部某绵羊慢病毒（ＯｖＬＶ）感染的羊场的绵羊用于本研究。用琼脂凝胶免疫扩散检查绵羊血清中对绵羊进行性肺炎（ＯＰＰ）病毒（ＯＰＰＶ）的抗体，结果表明有６例呈阳性，１例阴性，抗体效价在３年中呈下降趋势。４例血清学阳性边菜羊和１例阴性和田羊有不同程度的硬化性（纤维性）淋巴细胞性乳腺炎，小叶内有不等的淋巴细胞浸润，导管周围无淋巴滤泡形成，小叶间大量纤维组织增生。７例的肺、脑、关节、血管均无ＯｖＬＶ性特异性病变。从血清学阳性羊的外周血白细胞中未分离到ＯｖＬＶ。     

参与式方法在退耕还林中的应用

本文分析了退耕还林程序和山西省PAAF项目的经验.提出在制订退耕还林县级年度方案、具体实施过程和检查验收等阶段应用半结构访谈、村民大会、实施管理条例以及实施小组和监测小组等参与式工具.     

谈新国家标准《机械制图》中一些概念的科学性

国家标准机械制图中的概念应体现其科学性,即能反映客观实际和反映其不质属性。本文就新国标中的几个概念,阐明只有建立在科学基础上的术语、概念才能被各方面所接受,才有统一的实践基础。     

Scale of heterogeneity of forage production and winter foraging by elk and bison

The relationship between fine-scale spatial patterns of forage abundance and the feeding patterns of large ungulates is not well known. We compared these patterns for areas grazed in winter by elk and bison in a sagebrush-grassland landscape in northern Yellowstone National Park. At a fine scale, the spatial distribution of mapped feeding stations in 30 m × 30 m sites was found to be random where there were no large patches devoid of vegetation. In areas similar to the mapped sites, the underlying spatial distribution pattern of biomass was also determined to be random. At a broad scale, forage biomass differed among communities across the northern range but forage quality did not. These results suggest that ungulates are feeding randomly within forage patches (fine scale) but may select feeding sites based upon forage abundance at broader, landscape scales. Contrary to what has been suggested in other systems, ungulates were not overmatching at finer scales.     

Effects of area and isolation of woodland patches on herbaceous plant species richness across Great Britain

Richness of Ancient Woodland Indicator plant species was analysed in 308 woodland patches that were surveyed during the Countryside Survey of Great Britain carried out in 1998. The Countryside Survey recorded vegetation plots and landscape structure in 569 stratified 1 km sample squares and developed a remotely-sensed land cover map of the UK. Using these datasets, we tested the hypothesis that Ancient Woodland Indicator species richness in woodland fragments was limited by patch area, shape and spatial isolation and that woodland patches located in the lowland region of Great Britain would respond differently than those in the upland region. The variation in Ancient Woodland Indicator species richness in the British lowlands (n = 218) was mainly explained by patch area and two measures of connectivity, the length of hedgerows and lines of trees in the 1 km square and the area of woodland within 500 m of the vegetation plot. By contrast, variation in Ancient Woodland Indicator species richness in the British uplands (n = 90) was related to Ellenberg scores of the vegetation communities sampled – a surrogate for habitat quality – and no significant effect of spatial structure was detected. It therefore appears that the degree of fragmentation of woodland in the British lowlands limits the distribution of Ancient Woodland Indicator species, while in the uplands, failed colonisation is a matter of habitat quality rather than a result of landscape structure.This revised version was published online in May 2005 with corrections to the Cover Date.     

大熊猫放归计划框架与操作程序初探

本文依据IUCN/RSG关于物种放归的标准,借鉴麋鹿、普氏野马和扬子鳄等物种放归的成功经验,提出了大熊猫放归的基本内容和程序,即:足够的生物学和生态学的知识;适宜栖息地的选择;充足的释放动物种源;在实验的基础上,经过有效的工作小组的分析和综合,从潜在的栖息地的评估和选择,到小规模的释放试验性项目,长期监测,发展到正式放归项目实施。