野化培训大熊猫采食和人为砍伐对拐棍竹无性系种群更新的影响

亚高山竹类占据着野生大熊猫(Ailuropoda melanoleuca)食物组分的99%,竹子的生命周期与大熊猫的生活史密切相关,竹子的更新和生长直接影响着大熊猫的生存与保护.为了弄清大熊猫的采食利用和人为砍伐是否促进或制约竹子的繁殖更新,应用样方法、定位观察法,连续研究了卧龙自然保护区大熊猫栖息地内野化培训大熊猫采食、人为砍伐和对照样方中拐棍竹无性系种群的更新动态.结果表明,在相同种群数量和环境条件的基础上(p>0.05),被大熊猫采食竹子的比例为67.07%,致死率29.07%;人为砍伐竹子的比例为65.67%,致死率46.68%,可见与大熊猫采食相比,砍伐更为影响拐棍竹种群的生存.从出笋数量来看,不同处理方式有利于拐棍竹无性系种群的更新(p<0.05),尤其是人为砍伐措施大大提高了竹子的出笋率,但人为砍伐样方的竹笋质量(地径和株高生长)却远低于大熊猫采食和对照样方,未能达到大熊猫觅食的选择利用标准.不同年份之间,各种处理方式下的拐棍竹出笋数量波动较大(p=0.006～0.035),并随着恢复时间的延长,逐渐趋于相似(2007,p=0 825).不同处理方式之间,拐棍竹无性系种群的年补充率,各年份均具有显著性差异(p<0.05,除2007年外),年死亡率仅2003年和2004年有明显的差异(p<0.05),2005～2007年均不显著(p>0.05).拐棍竹无性系种群的年补充率与年死亡率之间表现出年补充率﹥年死亡率的格局(p<0.05),唯有大熊猫采食样方的2004年和2005年、人为砍伐和对照样方的2005年的年死亡率略高于年补充率(p>0.05),这表明拐棍竹无性系种群对大熊猫采食和人为砍伐具有无性系整合的补偿效应.     

黄龙大熊猫种群数量及年龄结构调查

１９９６年６￣１０月,在野外采用路线－聚类法对黄龙寺自然保护区内大熊猫种群数量进行了调查。结果表明：保护区内现有大熊猫２３只,竹林内生态密度为０．４３９只／ｋｍ＾２。此外,首次采用了离差平方和聚类的方法,将该种群划分为４个年龄组。其中幼年组个体上占１３．３３％,青年组个体占６．６７％,成年组个体占６０％,老年组个体占２０％。最后还对结果进行了讨论。并提出了保护措施。     

白水江自然保护区糙花箭竹天然林生物量与生产力的初步研究

 本文根据样方上测定糙花箭竹的地径、茎高、密度、茎重、枝条重、叶重和鞭系重资料,研究竹林生物量和生产力,并建立回归数学模型为：茎重Ws=160.942+0.227(D2NH) p<0.001 枝条重WB=76.008+0.039(D2NH) p<0.001 叶重WL＝80.643+0.051(D2NH) p<0.001 鞭系重WR=285.554+0.074(D2NH) p<0.001由方程估测出天然糙花箭竹林的各器官干重分别为茎7.558,枝条1.782,叶2.143,鞭系4.795t／ha。总生物量为16.278t／ha,平均净生产量为3.256t／ha。     

卧龙自然保护区典型生态系统服务时空变化研究

自然保护区作为生态系统服务的产生区和生物多样性保护的重点区,评估其关键生态系统服务,对提高保护区管理水平和生态保护与建设效率有重要意义。利用CASA模型、RUSLE模型、InVEST模型及水量平衡原理等方法分别定量评估了卧龙自然保护区2000年和2015年碳固定（NPP）、土壤保持、生境质量和水源涵养4种生态系统服务并分析了其时空分布及其变化特征,揭示了不同地形位梯度和土地利用类型上生态系统服务的差异,识别了生态系统服务的热点区域。研究结果揭示了2000-2015年4种生态系统服务及其变化的时空异质性：1）研究期间保护区4种生态系统服务供给量均有所增加,且增益面积大于减损面积;2）空间上,NPP、土壤保持和生境质量3种服务表现为东南高、西北低,水源涵养空间分布无明显规律,4种服务的空间分布特征均变化不大且保持相对稳定;3）4种生态系统服务空间分布及变化与地形位和土地利用类型有关。4种服务的高值和增益的优势分布区均位于较低地形位指数梯度上,以保护区东南部最为突出;林地和草地是对保护区生态系统服务贡献较大的土地利用类型,尤以林地突出;4）热点分析表明保护区东南部是主要的生态系统服务供给热点区,研究期间Ⅳ类热点区面积显著增加。结合研究区域生态系统特征和生态恢复与管理政策,探讨分析了目标生态系统服务时空变化的自然生态和社会经济驱动力,为本区域生态系统恢复和生物多样性保护提供依据和建议。     

Microphysiological systems: What it takes for community adoption

Microphysiological systems (MPS) are promising in vitro tools which could substantially improve the drug development process, particularly for underserved patient populations such as those with rare diseases, neural disorders, and diseases impacting pediatric populations. Currently, one of the major goals of the National Institutes of Health MPS program, led by the National Center for Advancing Translational Sciences (NCATS), is to demonstrate the utility of this emerging technology and help support the path to community adoption. However, community adoption of MPS technology has been hindered by a variety of factors including biological and technological challenges in device creation, issues with validation and standardization of MPS technology, and potential complications related to commercialization. In this brief Minireview, we offer an NCATS perspective on what current barriers exist to MPS adoption and provide an outlook on the future path to adoption of these in vitro tools.     

Do vine species in neotropical forests see the forest or the trees?

Questions: Is the occurrence of vine species in neotropical rain forests primarily determined by properties of the forest (environmental factors), by properties of the trees (tree species or tree size) or are vines randomly distributed? Location: Maya Biosphere Reserve, Guatemala. Methods: In five 1‐ha plots that span variation from unlogged forest to forest impacted by recurrent human disturbance we recorded the presence of all climbing vine species on every tree. The presence of all free standing vine species and 11 environmental variables were recorded in 100‐m² subplots. The relationship of host tree diameter and host tree identity on single tree vine species richness was investigated by GLM modelling. Partial redundancy analyses were used to partition the variation in vine species composition on two sources: environmental factors and tree species identity. Results: Single tree vine richness increased with increasing host tree DBH and differed significantly among host species. For climbing vines, the ratio of variation in subplot presence explained by tree species and by environmental variables was ca. 4:1 (in the most disturbed logged plots slightly lower), for free standing vines this ratio varied from 1:2 in the most disturbed logged plots to 9:1 in reserve plots, while a ratio of ca. 1:1 was found for all plots analysed together. Conclusion: Different tree species have different probabilities of being infested by vines. Vines see both the forest and the trees; the environment is more important in earlier developmental stages, properties of individual trees become more important from the time vines start to climb.     

Development of Health‐Related Waist Circumference Thresholds Within BMI Categories

Objective: To develop and cross‐validate waist circumference (WC) thresholds within BMI categories. The utility of the derived values was compared with the single WC thresholds (women, 88 cm; men, 102 cm) recommended by NIH and Health Canada. Research Methods and Procedures: The sample included adults classified as normal weight (BMI = 18.5 to 24.9), overweight (BMI = 25 to 29.9), obese I (BMI = 30 to 34.9), and obese II+ (BMI ≥ 35) from the Third U.S. National Health and Nutrition Examination Survey (NHANES III; n = 11, 968) and the Canadian Heart Health Surveys (CHHS; n = 6286). Receiver operating characteristic curves were used to determine the optimal WC thresholds that predicted high risk of coronary events (top quintile of Framingham scores) within BMI categories using the NHANES III. The BMI‐specific WC thresholds were cross‐validated using the CHHS. Results: The optimal WC thresholds increased across BMI categories from 87 to 124 cm in men and from 79 to 115 cm in women. The validation study indicated improved sensitivity and specificity with the BMI‐specific WC thresholds compared with the single thresholds. Discussion: Compared with the recommended WC thresholds, the BMI‐specific values improved the identification of health risk. In normal weight, overweight, obese I, and obese II+ patients, WC cut‐offs of 90, 100, 110, and 125 cm in men and 80, 90, 105, and 115 cm in women, respectively, can be used to identify those at increased risk.     

甘肃东大山自然保护区岩羊生态行为的初步观察

2004年7月和8月,通过样线调查、野外直接跟踪观察和瞬间取样的方法,对东大山自然保护区岩羊(Pseudois nayaur)的种群结构和生态行为进行了初步研究。在观察到的720只岩羊中,719只组成了50个群,最大的群82只,最小的群2只,平均群大小(14.38±15.83)只(n=50)。雌雄性比为1∶0.63,成年雌体、亚成体和幼体之比是1∶0.4∶0.24。岩羊的昼间活动中,上午和下午各有一个瞬间觅食高峰,分别在6:30时和15:30时,中午有一段较长时间的休息期。通过对一个46只岩羊群连续12 d的野外跟踪观察,发现该岩羊群昼间的活动范围基本上在1.47 km2内。对152个自然死亡的雄性岩羊头骨的分析表明,东大山雄性岩羊的自然死亡年龄在7.5~11.5龄,其中9.5龄是其自然死亡的高峰。     

云居山栓皮栎群落特征及多样性研究

栓皮栎群落是我国暖温带和亚热带落叶阔叶林的重要森林群落类型之一,也是赣北珍稀森林群落之一,在森林演替和植物资源利用中占有重要的地位。通过对江西云居山栓皮栎(Quercus variabilis)群落进行实地调查,采用区系分析、生活型谱分析、物种多样性和双向聚类等方法对其群落特征进行了研究,发现云居山自然保护区栓皮栎群落结构简单,层次明显,多样性程度不高。物种调查及区系研究结果显示,云居山栓皮栎群落维管束植物共计43科56属70种,植物区系主要以泛热带、东亚及北美间断、北温带分布为主,表现出从温带区系向热带区系过渡的特征;生活型谱以高位芽植物为主(占70%),其他生活型相对较少,反映出中亚热带森林以高位芽植物为主的特点。群落物种丰富度、多样性指数均为乔木层小于灌木层和草本层,均匀度指数分析表明,乔木层为聚集分布、灌木层和草本层为均匀分布。双向聚类分析表明,调查的5个样地均为栓皮栎群落,以乔木层物种多度可将5个样地分为3类,组成群落的24个主要物种可分为10类。     

海南大田国家级自然保护区鸟类考察初报

2001年10月至2002年9月,采用晨昏沿样带观察及用鸟网捕捉的方法对海南大田国家级自然保护区进行了鸟类资源考察。本次考察共记录鸟类75种,分属于12目30科,加上以往文献记载,该地区总计有鸟类13目36科92种,约占全国鸟类总数的6．97％。其中东洋界鸟类71种,古北界鸟类4种,广布种17种;繁殖鸟类65种(包括留鸟和夏候鸟),冬候鸟和旅鸟23种,居留期不清或迷鸟4种。该区域有许多被保护的鸟类,其中Birds to Watch收录2种,CITES收录5种,中国濒危物种红皮书收录10种,中国重点保护动物名录收录15种。