大熊猫染色体晚复制带研究

以培养的大熊猫外周血淋巴细胞为实验材料,在细胞培养终止前４ｈ加入ＢｒｄＵ（终浓度为１０μｇ／ｍｌ培养基）,对复制的染色体ＤＮＡ进行ＢｒｄＵ标记。掺入ＢｒｄＵ的染色体经吖啶橙（０．０５％）处理、紫外光照射、Ｇｉｅｍｓａ染色后,可在染色体上获得清晰的复制带纹。根据众多分裂相所显示的不同复制带型,可初步确定大熊猫每一染色体独特的晚复制带纹。在雌性个体的两个Ｘ染色体中,一条Ｘ染色体复制明显落后于另一Ｘ染色体,尤其在迟复制Ｘ染色体长臂近着丝粒区显现出较宽的晚复制带纹。     

大熊猫气味标记DNA的制备和序列分析

大熊猫气味标记在其个体间的通讯中具有重要意义。用不同方法收集了７只大熊猫个体的９个气味标记样品,运用Ｉｎｓｔａｇｅｎｅ Ｋｉｔ制备出了ＤＮＡ。采用ＰＣＲ扩增线粒体Ｄ－环区和细胞色素ｂ基因、Ｔｈｒ－ｔＲＮＡ基因片段并作序列分析。结果提示,不同收集方式所得气味标记样品均有ＤＮＡ,但用干棉花收集样品的方法最佳。该方法为大熊猫的遗传多样性研究提供了新的简捷有效的ＤＮＡ来源。     

Nature reserve group planning for conservation of giant pandas in North Minshan, China

Formation of nature reserve groups (NRGs) is an important approach for optimising spatial patterns in nature reserves and for improving the efficiency of nature reserve networks. In this study, based on habitat evaluation and connectivity analysis, the approach and method for optimising spatial patterns and functional zoning of reserves were analysed using the case study of giant panda (Ailuropoda melanoleuca) reserves in North Minshan. Results indicated that five panda nature reserves had been established, which formed a reserve group and covered 48.4% of panda habitat and three of five population components. Although the nature reserves were connected to each other, core zones were divided into seven isolated areas. These divisions can reduce the efficiency of protecting giant pandas in reserve systems. To optimise spatial patterns in nature reserves, one new reserve is proposed and it is recommended that core zones be expanded and merged into two areas, in accordance with the spatial distribution of the panda population. Three linkage areas are also proposed—for facilitating panda exchange and movement among different populations. The study is expected to provide a scientific basis for planning the development of nature reserves in this mountain range, to promote the establishment of nature reserve groups in other areas, and to optimise entire nature reserve systems in China.     

秦岭大熊猫冬春季节对巴山木竹竹林生长指标的选择

2004~2005年冬季的12月、1月和春季的4月、5月,在秦岭山系南坡佛坪自然保护区内就大熊猫对构成其主要栖息地和食物来源的巴山木竹竹林的选择进行研究后的结果表明:在冬季,大熊猫栖息地多为幼竹与死竹比例基本持平、密度稳定的巴山木竹竹林,主要取食老竹;在春季,大熊猫更偏好选择竹子密度和盖度略低、竹子粗壮高大、幼竹与竹笋比例高的竹林活动,主要取食幼竹。大熊猫春季栖息地幼竹比例通常高过死竹比例,竹林密度处于增长期。竹林进入发笋期后,稀疏、高大的竹林下的粗大竹笋成为大熊猫的主要食物来源。     

汶川地震对四川龙溪—虹口和唐家河自然保护区大熊猫栖息地利用格局的影响

2008年的汶川地震发生在大熊猫集中分布的区域,对大熊猫的栖息地造成了严重破坏.利用龙溪—虹口和唐家河两个国家级自然保护区地震前(2003～ 2007)和地震后(2008～ 2010)共计7年的大熊猫监测数据,就汶川地震对大熊猫栖息地利用格局的影响进行了分析.研究结果表明:(1)地震前5年,大熊猫对栖息地的利用格局在年间没有显著变化;(2)地震后的2年间,大熊猫对栖息地的利用格局在年间没有显著变化;(3)地震前后连续7年调查的样线中,大熊猫对栖息地的利用格局在年间没有显著变化;(4)在龙溪一虹口保护区,大熊猫对样线的利用与滑坡体的面积没有显著关系,即大熊猫对栖息地的空间利用没有受到滑坡体面积大小的显著影响;(5)虽然从现有资料发现地震对大熊猫栖息地的利用格局没有显著的影响,但仍然需要在震后加强对大熊猫及其栖息地的保护.     

Parasite Threat to Panda Conservation

The giant panda is a global symbol of wildlife conservation that is threatened by historic and current habitat loss. Despite a great deal of research on the physiology, reproductive biology, and diet of pandas in the wild and in captivity, there is little information on wild panda mortality. Here we integrate previously unavailable data on the mortality of wild pandas. We report on three recent phases of panda mortality: deaths due to bamboo flowering in the 1970s and 1980s, surprisingly extensive poaching in the 1980s and 1990s, and a parasitic infection over the past few years. Our analyses suggest that the current most significant threat to wild panda survival is disease due to extraintestinal migration (visceral larval migrans) by an ascarid nematode. We demonstrate that the probability of death of wild pandas being caused by this disease increased significantly between 1971 and 2005 and discuss the possible factors leading to the emergence of this disease. Electronic Supplementary Material The online version of this article (doi:) contains supplementary material, which is available to authorized users.     

洞庭湖流域麋鹿等哺乳动物濒危灭绝原因的分析及其对麋鹿重引入的启示

洞庭湖流域曾有亚洲象(Elephasmaximus)、犀(Rhinocerossp.)、麋鹿(Elaphurusdavidianus)、川金丝猴(Rhinopithecusroxellana)、长臂猿(Hylobatessp.)、大熊猫(Ailuropodamelanoleuca)、梅花鹿(Cervusnippon)、棕熊(Ursusarctos)等哺乳动物分布,但受古气候、古地理以及人类活动的影响,这些哺乳动物已在洞庭湖流域灭绝。这些哺乳动物的濒危和灭绝既受自然环境变化和灾变的影响,也与物种本身生物学特性和人类活动有关,尤其与人类捕杀和生境丧失有关。据古籍记载分析:在洞庭湖流域,亚洲象和犀于北宋末期灭绝或已南迁,而野生麋鹿、大熊猫、川金丝猴、长臂猿、梅花鹿和棕熊等于19世纪末灭绝。根据我们对30个自然保护区或森林公园野生动物资源实地调查的结果,在洞庭湖流域已记录到21种国家重点保护哺乳动物,其中有5、6、10种哺乳动物分别处于“极危”、“濒危”、“易危”等级,这表明物种濒危的过程仍在继续。导致这些现生哺乳动物濒危的主要原因是生境丧失、人类猎捕、环境污染等,而人类活动干扰对现生濒危物种存活的影响越来越大。洞庭湖流域重引入麋鹿需采取人类协助生存策略:提供足够的且受洪水影响小的适宜生境、保证稳定的奠基者种群数量、减少人为干扰、调控种群密度、实施社区共管和生计替代项目、加强疾病防治、完善保护措施、加大保护基金投入、加强生境监测和湿地恢复等。     

小相岭大熊栖息地干扰调查

强烈的人类干扰是大熊猫濒危的主要原因。本于2001年6～7月对四川省小相岭大熊猫栖息地内竹子开花、火灾、滑坡3种自然干扰类型和采伐、放牧、采药、公路、偷猎、割竹采笋、耕作、开矿和旅游9种人类干扰类型进行了调查。调查样方878个,干扰发生在海拔1800～4000m。结果表明：自然干扰都不严重,干扰比例最高的竹子开花,也仅占1．14％。采伐、放牧、采药和公路是主要人类干扰类型,分别占调查总样方的34．9％,26．3％,5．1％和4．2％。干扰最严重的地段是海拔3000～3499m,采伐样方的49．67％,放牧样方的47．19％,采药样方的31．11％均发生在该段,同时有48．89％的大熊猫活动痕迹样方也在该海拔。近年来,由于国家实施“天然林保护工程”,采伐已不再是主要干扰,而放牧、采药和偷猎等活动在短时间内仍不会减少。