唐家河自然保护区大熊猫种群数量及栖息地的移动

本文根据大熊猫季节性活动规律特点,应用海拔高度路线调查法,全面收集唐家河自然保护区大熊猫的比较新鲜粪便,计获１２４个粪样材料,提取ＤＮＡ作ＤＮＡ指纹图,经微机检测,保护区有大熊猫３７只,个体数量与粪样采集量之比为１∶３３５１４,有６个家系,雌兽２１只,雄兽１６只。并搞清了保护区生态环境质量,箭竹遭受病虫害的程度,洪水对栖息地的影响,特别对引起大熊猫数量减少及栖息地移动等原因,作了较为详细的分析。     

不同EGF和胰岛素水平对体外培养的大熊猫皮肤成纤维细胞的影响

用DME∶Ham sF12(1∶1)培养液,添加3个水平的EGF和2个水平的胰岛素,组合成6种培养体系(CS)分别培养大熊猫皮肤成纤维细胞。通过对细胞生长速度和染色体数目变异率进行测定,测得在添加10μg/ml的胰岛素和40 ng/ml的表皮生长因子的培养体系中,以1.673±0.185×105/ml密度接种细胞,经3.5天,密度达到6.890×105/ml,其生长速度最快;染色体数目为二倍体的百分率为75.77%。综合衡量,CS-5在本研究中更适合大熊猫皮肤成纤维细胞的培养。     

Modeling activity patterns of wildlife using time‐series analysis

The study of wildlife activity patterns is an effective approach to understanding fundamental ecological and evolutionary processes. However, traditional statistical approaches used to conduct quantitative analysis have thus far had limited success in revealing underlying mechanisms driving activity patterns. Here, we combine wavelet analysis, a type of frequency‐based time‐series analysis, with high‐resolution activity data from accelerometers embedded in GPS collars to explore the effects of internal states (e.g., pregnancy) and external factors (e.g., seasonal dynamics of resources and weather) on activity patterns of the endangered giant panda (Ailuropoda melanoleuca). Giant pandas exhibited higher frequency cycles during the winter when resources (e.g., water and forage) were relatively poor, as well as during spring, which includes the giant panda's mating season. During the summer and autumn when resources were abundant, pandas exhibited a regular activity pattern with activity peaks every 24 hr. A pregnant individual showed distinct differences in her activity pattern from other giant pandas for several months following parturition. These results indicate that animals adjust activity cycles to adapt to seasonal variation of the resources and unique physiological periods. Wavelet coherency analysis also verified the synchronization of giant panda activity level with air temperature and solar radiation at the 24‐hr band. Our study also shows that wavelet analysis is an effective tool for analyzing high‐resolution activity pattern data and its relationship to internal and external states, an approach that has the potential to inform wildlife conservation and management across species.     

Isolation and characterization of microsatellite loci for the red panda,Ailurus fulgens

We report on the isolation and characterization of 10 microsatellites in the red panda Ailurus fulgens from genomic DNA‐enriched libraries. Twenty‐one microsatellites were screened from the libraries, and 10 of the screened microsatellites were polymorphic. The number of observed alleles for each locus in 24 individuals ranged from three to 12, and the expected and observed heterozygosity was 0.60–0.90 and 0.50–1.00, respectively. These markers should prove a useful tool for the study of genetic variation in red panda in the future.     

Influences of mating groups on the reproductive success of the Southern Sichuan Red Panda (Ailurus fulgens styani)

The reproduction of female red pandas under three different husbandry conditions (monogamy, polygamy, and polyandry) was studied at the Chengdu Research Base for Giant Panda Breeding, and Chengdu Zoological Park, China. We monitored the fecal steroid profiles of seven females by radioimmunoassay in order to understand how the different mating groupings affect the animals' reproductive success. Of the seven females studied, all gave birth except the one that was kept in the polyandrous group. Although fecal estradiol metabolites exhibited several peaks during estrus, only one coincided with mating behavior. Fecal progesterone metabolites did not display a sustained rise in the absence of mating behavior, even though estradiol displayed a peak of secretion. This suggests that the red panda may be an induced ovulator. During gestation, fecal progesterone metabolites were maintained at a comparatively high level, and were much higher than those of nonpregnant females. The female in the polyandrous group showed an abnormal estradiol metabolite profile, with a level that was four to five times higher than those of the females in the polygynous groupings. It was observed that this female always escaped and hid in the trees to avoid courtships with males, and did not give birth. This phenomenon suggests that polyandrous groupings may be unsuitable for successful reproduction in captivity. Zoo Biol 24:169–176, 2005. © 2005 Wiley‐Liss, Inc.     

凉山山系小熊猫(Ailurus fulgens)分布区景观格局

根据2000～2001年对凉山山系主山脊7个县小熊猫野外分布调查数据,利用“3S”技术对凉山山系小熊猫分布区进行了确定,估算出分布区面积为219055hm^2,占山系研究区域面积17．8％。利用景观空间格局定量化分析软件FRAGSTATS,分析了小熊猫分布区景观格局的组成、各类型斑块特征、不同类型斑块间空间分布关系。结果表明,栖息地景观边缘褶皱程度低,趋于平整,景观丰富度大;森林斑块间的结构连通性较好,各类型斑块聚集度较高。小熊猫生境内部破碎化程度较低,森林结构连接程度高,有适宜生境面积为160249．5hm^2,占分布区面积的73．15％,生境中存在3个脆弱区域,特别是美姑-峨边公路通过的椅子垭口区域需要引起极大的关注。     

岷山地区大熊猫(Ailuropoda melanoleuca)生境影响因子连通性及主导因子

岷山地区是大熊猫保护的关键地区.运用图论分析法研究了岷山地区大熊猫生境影响因子,及其相互作用关系.结果表明:在岷山地区,12个影响因子66对组合中,47.0%的影响因子间存在直接的联系,其中89.2%的影响具有增大效应,这说明人类活动对大熊猫生境的影响具有协同增大效应,并占主导地位.研究发现,在影响因子关系集中,存在强连通性的子集K={(TD);(RB);(MI);(HPL);(AP);(AD);(SR);(TH);(FC)},这表明近期进行的旅游景点开发,公路建设,采矿,高压电线走廊建设,以及传统的农业开发,畜牧业,薪柴采集等影响因子之间存在着强烈相互作用关系,这些人类活动还会将其他人类活动对大熊猫生境的影响放大,加剧其对大熊猫生境的不利影响,是影响岷山地区大熊猫生境的主导因素.研究还表明如果不能对主导因子进行有效的控制,很难有效地保护岷山地区大熊猫生境.研究表明图论分析法是研究大熊猫生境影响因子的一个有效工具,有助于明确影响熊猫生境的主导和关键因子,为制定有效的大熊猫保护策略提供科学依据.     

A reliable, non-invasive PCR method for giant panda (Ailuropoda melanoleuca) sex identification

We developed an inexpensive, fast and reliable PCR method for sex identification of giant panda (Ailuropoda melanoleuca) by using one pair of primers to co-amplify homologous fragments with size polymorphism that located at amelogenin (AMEL) exon 5. In giant panda, a 63 bp deletion in exon 5 of Y-linked allele provides a significant discrimination between AMELX and AMELY, thus the amplification products can be distinguished simply by agarose gel electrophoresis, exhibiting sex-specific banding patterns (male: 237 bp, 174 bp; female: 237 bp). Both blood and feces samples from known-sex giant pandas were successfully amplified. Cross species test also revealed that this method could be applied to other Ursidae species. These authors contributed equally to this work.     

放牧对冶勒自然保护区大熊猫生境的影响

四川冶勒自然保护区周边村民的牲畜基本上都在保护区内放养。为研究放牧和大熊猫对竹类的利用及放牧强度与竹类的关系 ,利用Forageratio选择指数 ,Pearson相关分析和联列表独立性检验 ,对调查数据进行分析。结果表明 ,大熊猫活动区海拔为 2 870～ 390 0m ,并喜欢选择竹类盖度为 5 0 %～ 10 0 % ,竹类高度 2～ 3m ,竹类生长状况好的竹林。而放牧海拔为 2 70 0～ 4 0 0 0m ,放牧对竹类的盖度、高度、生长状况没有选择性 ,为随机利用。放牧海拔与大熊猫活动海拔无显著相关。大熊猫在放牧生境活动的频率较低 ;放牧生境中竹类的成竹平均密度和竹子平均密度都低于大熊猫活动生境 ,枯死竹比例高于大熊猫活动生境。放牧强度与竹类的有、无和竹类盖度是相关联的 ,大熊猫出现与否也与放牧活动相关联 (在 95 %的置信度 ,P <0 0 5 )。放牧强度强的生境没有大熊猫活动 ,竹子的盖度也较低。由于放牧活动对竹类的生长和盖度造成影响 ,从而影响大熊猫对放牧生境的利用 ,在保护区内应采取一定的措施控制放牧活动。     

Microsatellite variability reveals the necessity for genetic input from wild giant pandas (Ailuropoda melanoleuca) into the captive population

Recent success in breeding giant pandas in captivity has encouraged panda conservationists to believe that the ex situ population is ready to serve as a source for supporting the wild population. In this study, we used 11 microsatellite DNA markers to assess the amount and distribution of genetic variability present in the two largest captive populations (Chengdu Research Base of Giant Panda Breeding, Sichuan Province and the China Research and Conservation Center for the Giant Panda at Wolong, Sichuan Province). The data were compared with those samples from wild pandas living in two key giant panda nature reserves (Baoxing Nature Reserve and Wanglang Nature Reserve). The results show that the captive populations have retained lower levels of allelic diversity and heterozygosity compared to isolated wild populations. However, low inbreeding coefficients indicate that captive populations are under careful genetic management. Excessive heterozygosity suggests that the two captive populations have experienced a genetic bottleneck, presumably caused by founder effects. Moreover, evidence of increased genetic divergence demonstrates restricted breeding options within facilities. Based on these results, we conclude that the genetic diversity in the captive populations is not optimal. Introduction of genetic materials from wild pandas and improved exchange of genetic materials among institutions will be necessary for the captive pandas to be representative of the wild populations.