一夫一妻西黑冠长臂猿的群体活动及其影响因素

高海拔栖息地中灵长类动物的行为适应一直以来都是灵长类研究中的重点内容,同物种在不同栖息地的行为差异也成为近年的热点问题。西黑冠长臂猿(Nomascus concolor)是我国国家一级重点保护野生动物,也是我国长臂猿科动物中种群数量最大的物种,滇中哀牢山、无量山是该物种的集中分布区。哀牢山和无量山的西黑冠长臂猿栖息地存在显著差异,且其社会组织不同。本研究首次报道了在哀牢山高海拔栖息地中一个一夫一妻长臂猿群体的活动时间分配和食性季节性变化。2014—2015年,采用3 min间隔瞬时扫描法记录了长臂猿的行为和食性,468 h的行为数据结果表明,移动行为比例最高38.1%,其次是休息行为36.4%,取食行为23.3%,最少为鸣叫行为1.9%和其他行为1.3%。3 784次取食行为可辨识食物类型,总体上叶类食物占41.1%,其次是果实类食物33.3%,花类食物21.0%,附生植物3.9%,其他食物0.6%。长臂猿的时间分配和食性在雨季和旱季均具有显著差异,在低温旱季,长臂猿增加休息时间,减少移动时间,提高叶类和花类食物的取食比例;在高温雨季,长臂猿增加移动时间,减少休息时间和取食时间,取食更...     

滇南、滇东南黑冠长臂猿分布与数量

滇南、滇东南曾是黑冠长臂猿广泛分布的地区之一。为掌握该地区近年黑冠长臂猿分布及种群数量现状,从2003年7月~2004年12月,采用访问调查及利用鸣声定位法进行了实地调查。调查结果显示,在近40000km2的范围内,东黑冠长臂猿(Nomascussp.cf.nasutus)在云南境内可能已消失;西黑冠长臂猿(N.concolor)亦仅发现4~7个种群,且孤立分布于3个地区(金平芭蕉河2群6只,金平西隆山1-2群,绿春黄连山1~3群,总计不超过25只),而在江城牛倮河自然保护区、马关古林箐自然保护区、麻栗坡老君山自然保护区及屏边大围山自然保护区可能已绝迹。滇南、滇东南黑冠长臂猿分布区缩小及种群数量剧减,主要与栖息地丧失及过度捕猎有关。     

高黎贡山赧亢白眉长臂猿春季栖息地利用

2006年3月24日—5月6日,在高黎贡山赧亢片区共设置利用样地与可利用样地各30个,跟踪观察白眉长臂猿栖息地利用行为。定性因子分析表明,白眉长臂猿偏爱在东坡(Ei=0.344)活动,可能与其能提供避风的温暖微生境有关;偏爱栓皮栎(Ei=0.455)和拟樱叶柃(Ei=0.068)等乔木,可能是由于这些树种的树冠面积大,可为白眉长臂猿提供连续的移动路线和大的活动空间。定量因子分析表明,利用和可利用样地中共有12个因子(坡度,乔木和竹平均高度,乔木平均胸围,乔木和灌木盖度,乔木、竹和藤本密度,距水源、道路和草果地距离)存在显著差异,说明白眉长臂猿对栖境的空间结构具有高度的选择性。判别分析结果显示,坡度、乔木平均胸围、竹密度、距水源距离和乔木平均高度是判别利用和可利用样地的关键因子,即为影响其生境利用的主要因子,判别正确率为98.3%。作为树栖灵长类,具有一定基面积的连续乔木[高度(14.14±3.19)m,胸围(90.72±26.12)cm]树冠层是白眉长臂猿的适宜生境;较大的坡度(39.98±8.10°)减少了来自地面的干扰;而竹林是白眉长臂猿春季重要的取食地。     

云南临沧邦马山西黑冠长臂猿种群历史及现状

云南临沧邦马山是西黑冠长臂猿滇西亚种Nomascus concolor furvogaster重要分布地之一,但其种群现状一直没有系统的调查。从2013年10月至2014年1月及2014年5月,通过历时86 d对邦马山西黑冠长臂猿种群和分布现状的野外调查(包括访问调查和实地调查:鸣声定位法和样线法),首次绘制出该地区西黑冠长臂猿历史分布格局和变迁状况。西黑冠长臂猿曾广泛分布于邦马山大部分林区,数量在30群以上;20世纪60年代至20世纪末,因自然灾害、毁林开荒造成的森林破坏和猎杀导致邦马山长臂猿数量锐减至10群以下。目前,邦马山西黑冠长臂猿已从绝大部分原始分布区消失,整个邦马山仅2个地点(勐撒小邦马和芒洪大鹿山)可能分别有1群西黑冠长臂猿残存,其种群现状是西黑冠长臂猿已极为稀少,处于灭绝的边缘。调查发现,保护区内和周边林区仍存在较多的偷猎和砍伐等人为干扰现象,严重威胁残存的西黑冠长臂猿群体以及其他野生动物的生存和发展。作为澜沧江省级自然保护区的核心组分,邦马山亟需成立专门的保护区管理机构,以有效保护该地区的动植物资源和生态系统。     

高黎贡山赧亢白眉长臂猿春季栖息地利用

2006年3月24日—5月6日，在高黎贡山赧亢片区共设置利用样地与可利用样地各30个，跟踪观察白眉长臂猿栖息地利用行为。定性因子分析表明，白眉长臂猿偏爱在东坡(E_i=0.344)活动，可能与其能提供避风的温暖微生境有关；偏爱栓皮栎(E_i=0.455)和拟樱叶柃(E_i=0.068)等乔木，可能是由于这些树种的树冠面积大，可为白眉长臂猿提供连续的移动路线和大的活动空间。定量因子分析表明，利用和可利用样地中共有12个因子(坡度，乔木和竹平均高度，乔木平均胸围，乔木和灌木盖度，乔木、竹和藤本密度，距水源、道路和草果地距离) 存在显著差异，说明白眉长臂猿对栖境的空间结构具有高度的选择性。判别分析结果显示，坡度、乔木平均胸围、竹密度、距水源距离和乔木平均高度是判别利用和可利用样地的关键因子，即为影响其生境利用的主要因子，判别正确率为98.3%。作为树栖灵长类，具有一定基面积的连续乔木［高度（14.14±3.19）m，胸围（90.72±26.12）cm］树冠层是白眉长臂猿的适宜生境；较大的坡度(39.98±8.10°)减少了来自地面的干扰；而竹林是白眉长臂猿春季重要的取食地。     

高黎贡山大塘白眉长臂猿春季栖息地利用及与赧亢的比较

2007年3月9日～4月7日调查了高黎贡山大塘片区白眉长臂猿的生境利用情况.对1雌1雄 (均为成体) 家群和1只雌性独猿跟踪观察.设置利用样地和对照样地各30个,测量了4个定性因子和19个定量因子.判别分析结果显示,在大塘影响白眉长臂猿春季生境利用的关键因子是藤本密度和坡度2个因子;影响赧亢与大塘白眉长臂猿的则是距空旷地距离、竹子平均高度和距水源距离等3个因子.据地形因子分析结果,大塘和赧亢的白眉长臂猿对避风和趋阳坡有共同需求.比较两地白眉长臂猿对与植被结构有关的8个生态因子的利用结果提示,赧亢适宜白眉长臂猿栖息的生境呈破碎化分布,而大塘的植被均匀性和完整性较高.两地白眉长臂猿对优势乔木的选择都具有相同的外貌形态特征,树形高大、树冠连续、郁闭度高的乔木可为它们提供更多的移动路线、更广的活动空间和更好的隐蔽条件.白眉长臂猿对两个分布区林下竹灌层选择差异的原因一方面是人为干扰强度不同所致,另一方面是对林下竹灌层的利用方式不同.藤本是白眉长臂猿在乔木层与竹灌层之间活动的主要交通媒介和连接纽带.人为干扰强度的不同亦是导致两地白眉长臂猿生境利用差异的重要原因之一.     

中国长臂猿科动物的分类和保护现状

根据最新的长臂猿科分类系统和近年来开展的多次长臂猿调查,本文对我国长臂猿科的分类和保护进行了全面的回顾和综述,将为以后中国长臂猿的研究和保护提供基础资料。长臂猿科(Hylobatidae) 分为4 个属(Nomascus,Symphalangus,Hylobates, Hoolock ) 17 个种,其中我国分布有3 属6 种: 西黑冠长臂猿(N. concolor)、东黑冠长臂猿(N. nasutus)、海南长臂猿(N.hainanus)、北白颊长臂猿(N. leucogenys)、东白眉长臂猿(Hoolock leuconedys)和白掌长臂猿(Hylobates lar)。长臂猿曾经广泛分布于我国大部分地区,受栖息地丧失、退化和猎杀等因素的影响,目前长臂猿仅分布于云南、广西和海南等地。我国长臂猿的保护形势十分严峻,白掌长臂猿和北白颊长臂猿可能已经从中国消失;东黑冠长臂猿和海南长臂猿的数量都不足30 只,接近灭绝边缘;东白眉长臂猿的数量不足200 只;即使是数量最多的西黑冠长臂猿,其数量也仅有1 000 至1 300 只。严格执法、意识教育、科普宣传、长期的科学研究将有利于我国的长臂猿保护。     

云南中部无量山黑长臂猿(Nomascus concolor jingdongensis)栖息地乔木层物种多样性和结构特征

无量山是黑长臂猿景东亚种的唯一分布区,现栖息着98群500余只黑长臂猿。长臂猿是典型的树栖性灵长类动物,通过对无量山西坡大寨子地区250个样方的调查,分析了随海拔梯度升高,黑长臂猿栖息地植被乔木层物种多样性和结构的变化情况。共记录乔木111种,隶属于33科;木质藤本23种,隶属于18科。其中优势科主要有樟科(Lauraceae)、木兰科(Magnoliaceae)、壳斗科(Fagaceae)、山茶科(Theaceae)和杜鹃花科(Ericaceae)。根据不同海拔乔木层物种组成的差异,该区可划分为半湿润常绿阔叶林(2100~2300m)和中山湿性常绿阔叶林(2400~2600m)两种植被类型。多样性指数(Shannon-Wiener指数)随海拔升高在两种植被类型中均呈下降趋势;均匀度指数(Pielou指数)在半湿润常绿阔叶林中呈下降趋势,在中山湿性常绿阔叶林中无明显变化。半湿润常绿阔叶林中,阳坡的乔木物种多样性低于阴坡;而阳坡物种多样性在两种植被类型间差异显著。随着海拔的升高,乔木层的平均高度和上层乔木(Ⅰ层)的比例均逐渐降低,但下层乔木却呈上升趋势。6种优势乔木树种的种群年龄结构分析表明,该区植被的乔木层呈现稳定增长的趋势。     

云南哀牢山平河黑长臂猿栖息地乔木结构分析

采用样方方法对栖息于云南省哀牢山平河(E101°17′16.1″,N24°20′09.5″,海拔2600m)的黑长臂猿(Nomascus concolor)栖息地乔木层结构进行了调查。调查中共记录到乔木57种隶属于23科37属;木质藤本植物9种隶属于6科8属。优势科主要为杜鹃花科(Ericaceae)、木兰科(Magnoliaceae)、山茶科(Theaceae)和壳斗科(Fagaceae)植物。主要树种重要值排序表明,露珠杜鹃(Rhododendron irroratum)为该地区最主要的优势种,在各坡位中均有广泛分布。乔木的多样性指数、均匀度指数在沟底明显降低,而乔木1层和2层所占的比例以及木质藤本的平均多度均随着坡位的下降而升高。与其他地区的长臂猿相比,哀牢山黑长臂猿的活动程度较低(10—22m),果实性食物种类较少。     

贺兰山岩羊冬春季取食生境的比较

2003年11～12月和2004年4～6月,在贺兰山设定了25条固定样线,采用直接观察法对岩羊冬春季的取食生境选择进行了研究。结果表明,岩羊冬季对12种取食生境生态因子有选择性,偏爱选择位于山地疏林草原带,优势乔木为灰榆,乔木密度〈4株、高度4～6m,灌木密度〉5株、高度〉1．3m,食物质量〉50g,人为干扰距离〈500m,距裸岩距离〈2m的地方取食。而春季对11种取食生境生态因子有选择性,偏爱选择山地疏林草原带,优势乔木为灰榆,乔木密度〈4株、高度〈6m,灌木密度5～10株、高度1．3～1．7m,食物质量〉100g,海拔高度〈2000m,距水源距离〈500m,隐蔽级50％～75％的地点。冬春季岩羊对植被类型、地形特征、优势乔木、乔木密度、乔木高度、灌木密度、灌木距离、食物丰富度、坡向、坡度、距水源距离、人为干扰距离和隐蔽级的选择存在显著差异。主成分分析表明,冬季第1主成分的贡献率达24．493％,其中绝对值较大的权系数出现在植被类型、优势乔木、乔木高度、乔木距离、灌木密度、灌木高度、海拔高度、距水源距离和人为干扰距离等生态因子：春季第1主成分的贡献率达28．777％,其中绝对值较大的权系数出现在植被类型、乔木距离、灌木高度、灌木距离、食物丰富度、海拔高度和人为干扰距离等生态因子。随着北方地区冬春季食物数量和质量的剧烈变化,贺兰山岩羊对取食生境的利用对策也将发生一定程度的改变,与其他分布区的岩羊相比,贺兰山独特的地理位置和特殊生境使其在取食生境选择上存在很大差异。     

Population and distribution of western black crested gibbon (Nomascus concolor) at Ailao Mountain, Xinping, Yunnan

The western black crested gibbon (Nomascus concolor) is mainly distributed in Yunnan, China. Ailao Mountain is located in central Yunnan and divided into three prefectures and six counties. This mountain forms the principle distribution range for western black crested gibbon; however, there are no published data on the gibbon population inhabiting the Xinping administrative. Take the interview results conducted in 2007 and 2009 with local people as the reference, this study conducted an extensive field survey covering all possible habitats from November 2009 to January 2010 using call surveys. Among the one hundred and twenty-four gibbon groups which were confirmed across the Ailao Mountain, the largest known population of western black crested gibbons yet, 85 groups inhabit the national nature reserve and adjacent national forest, 30 groups inhabit the provincial nature reserve and nine groups inhabit the collective forest located outside the reserve and national forest. We found that the western black crested gibbons here have a patchy distribution pattern and occur at higher densities in certain areas. Moreover, the population distribution density and elevation gradient distribution decline from north to south. The results also demonstrated the importance of Ailao Mountain in the western black crested gibbon protection.     

广西邦亮东黑冠长臂猿新群体的发现及种群数量现状

东黑冠长臂猿是极度濒危物种,全球种群数量极其稀少。2015年5月和8月,采用在固定地点监听鸣叫的方法在广西邦亮长臂猿国家级自然保护区内对东黑冠长臂猿开展两次实地调查,发现在中国境内形成了由1只成年雄性,2只成年雌性和1只婴猿组成的新群体。这是自2006年该物种在中国被重新发现后,首次在中国境内发现形成新群体。中国境内东黑冠长臂猿的种群数量也由3群22只,增长到4群26只。有限的栖息地可能是未来限制东黑冠长臂猿新群体形成的主要因素之一,所以栖息地恢复对东黑冠长臂猿种群数量增长尤为重要。放牧不利于栖息地恢复,要逐步减少,进而杜绝在保护区内放牧。另外,东黑冠长臂猿跨国界分布,中越两国政府之间应加强协调,避免在保护区内实施对栖息地不利的边境管理活动。如果两国间出现种群隔离,对东黑冠长臂猿种群数量的增长将会非常不利。     

东黑冠长臂猿鸣叫声谱分析

2007 年9 月至2009 年6 月,利用Sony TC - D5 Pro2 录音机、Sony C - 76 指向性话筒和Sony 录音磁带对广西邦亮自然保护区3 群东黑冠长臂猿的鸣叫进行了录音,对每群录音效果较好的5 个声音用Signal/ RTS 4.0 软件进行声谱分析。结果表明:东黑冠长臂猿叫声的频率较高,最高频率已经达到甚至超过了5 kHz;雄性的鸣叫声由起始音(boom)、简单的重复音节(aa notes)、调节前音节(pre-modulated note)和调节音句(modulated phrases)组成,雌性长臂猿一般只会发出一种固定而刻板的激动鸣叫,二者互相配合组成结构复杂的二重唱。通常,二重唱由成年雄性发起和结束,并占主导地位。同时,将东黑冠长臂猿二重唱的声谱结构与近缘种西黑冠长臂猿和海南长臂猿进行比较,结果显示雄性和雌性的叫声、以及二者配合发出的激动鸣叫序列在三者之间都有明显差异。因此,从声谱特征角度可以有效论证这三种长臂猿独立物种的分类地位。     

云南哀牢山国家级自然保护区景东辖区黑长臂猿种群数量和分布

为掌握哀牢山国家级自然保护区景东县辖区黑长臂猿种群数量和分布状况,2005年9～11月采用访问调查法及鸣声定位法对该区域进行了调查。调查结果显示:该区域内20世纪50～80年代,在19个地区曾有黑长臂猿分布,但现在黑长臂猿分布范围已大为减少,目前仅在9个地区发现有9群黑长臂猿。50年代至今至少有13只黑长臂猿被猎杀。狩猎和栖息地破坏是造成该区域黑长臂猿种群数量减少及分布范围缩小的主要原因。     

Gibbons (Nomascus gabriellae) provide key seed dispersal for the Pacific walnut (Dracontomelon dao), in Asia's lowland tropical forest

Understanding the mutualisms between frugivores and plants is essential for developing successful forest management and conservation strategies, especially in tropical rainforests where the majority of plants are dispersed by animals. Gibbons are among the most effective seed dispersers in South East Asia's tropical forests, but are also one of the highly threatened arboreal mammals in the region. Here we studied the seed dispersal of the Pacific walnut (Dracontomelon dao), a canopy tree which produces fruit that are common in the diet of the endangered southern yellow-cheeked crested gibbon (Nomascus gabriellae). We found that gibbons were the most effective disperser for this species; they consumed approximately 45% of the fruit crop, which was four times more than that consumed by macaques – the only other legitimate disperser. Gibbons tracked the temporal (but not spatial) abundance of ripe fruits, indicating this fruit was a preferred species for the gibbon. Both gibbons and macaques dispersed the majority (>90%) of the seeds at least 20 m away from parent crowns, with mean dispersal distances by gibbons measuring 179.3 ± 98.0 m (range: 4–425 m). Seeds defecated by gibbons germinated quicker and at greater rates than seeds spat by macaques, or in undispersed fruits. Gibbon-dispersed seeds were also more likely to be removed by unknown seed predators or unknown secondary dispersers. Overall, gibbons play a key role in the regeneration of the Pacific walnut. Our findings have significant implications both for the management of the Pacific walnut tree dominating tropical rainforest as well as the reintroduction program of the Southern yellow-cheeked crested gibbon.     

Pileated Gibbon Density in Relation to Habitat Characteristics and Post‐logging Forest Recovery

ABSTRACT Although it is known that forest loss and degradation negatively impact most forest‐dwelling primates, such relationships are difficult to quantify because many primates are difficult to survey over large areas. Furthermore, recovery times are also difficult to assess due to a lack of long‐term data. Here, we determined how forest characteristics and habitat disturbance correlate with the abundance of pileated gibbons, Hylobates pileatus. We studied a population in Khao Ang Rue Nai Wildlife Sanctuary in southeastern Thailand, assessed its density using an auditory method combined with distance sampling at 24 randomly placed sample sites. In addition, we determined how simple forest structural characteristics and habitat disturbance correlate with the gibbon abundance. Average gibbon density per site was 1.02 ± 0.16 (SE) groups/km² (range 0–2.74). Bivariate analyses indicated that densities depended on food tree biomass, level of disturbance, evergreen forest cover, time since protection, and distance to the sanctuary boundary. Multiple regression analysis suggested evergreen forest cover and distance to boundary were the most influential factors. Because evergreen forest cover, time since protection, and habitat disturbance are correlated, these results suggest a direct dependence of gibbon densities on mature, undisturbed evergreen forest. While gibbons can persist in disturbed areas if the forest is protected, it appears that recovery to previous densities may take decades. We suggest that this is due to the slow pace of forest regeneration and/or poor recovery potential of gibbons.     

Habitat characterization of western hoolock gibbons Hoolock hoolock by examining home range microhabitat use

Conserving a species depends on an understanding of its habitat requirements. Primatologists often characterize the habitat requirements of primates using macroscale population-based approaches relying on correlations between habitat attributes and population abundances between sites with varying levels of disturbance. This approach only works for species spread between several populations. The populations of some primates do not fulfill these criteria, forcing researchers to rely on individual-based (microscale) rather than population-based approaches for habitat characterization. We examined the reliability of using micro-scale habitat characterizations by studying the microhabitat preferences of a group of wild western hoolock gibbons (Hoolock hoolock) in order to compare our results to the habitat preferences of western hoolock gibbons identified during a macroscale study of populations across Bangladesh. We used stepwise discriminant analysis to differentiate between the areas of low, medium, and high usage based on microhabitat characteristics (tree species availability, altitude, canopy connection, distance from forest edge, and levels of human disturbance). The gibbons used interior forest habitat with low food tree availability most frequently for sleeping and socializing, and used edge habitat containing high food tree availability for medium periods for feeding. These results indicate that the gibbons prefer interior forest but are frequently forced to visit the forest edge to feed. Therefore, the optimal habitat would be interior forest away from human disturbance with high sleeping-tree and feeding-tree availability. These habitat preferences are consistent with the habitat attributes of Bangladesh’s largest remaining western hoolock gibbon populations, which live in areas containing low agricultural encroachment and high food-tree availability. Microhabitat use studies can be used to characterize the habitat requirements of a species, but should include multiple scales of analysis wherever possible.     

Food selection in relation to nutritional chemistry of Cao Vit gibbons in Jingxi,China

The Cao Vit gibbon (Nomascus nasutus) has only one population with about 110 individuals living in a degraded karst forest along the China–Vietnam border. Investigation of food choice in relation to chemical nutrition will offer important insights into its conservation. We studied the food choice of two groups of Cao Vit gibbons using instantaneous scan sampling in Bangliang National Nature Reserve, Guangxi, China, over 4 years, and analyzed the chemical components (total nitrogen, TN; water-soluble sugar, WSS; crude fat, CF; neutral detergent fiber, NDF; acid detergent fiber, ADF; acid detergent lignin, ADL; condensed tannin, CT; and ash) of 48 food plant parts and 22 non-food plant parts. Fruits and figs that are rich in sugar are important food resources for gibbons. For other food types, flowers are a good source of total nitrogen and carbohydrates, and leaves and buds provide sources of protein and minerals. Cao Vit gibbons selected fruits that contain less total nitrogen, less acid detergent fiber and more water-soluble sugar than non-food fruits. Several food species that were heavily consumed by Cao Vit gibbons are suggested as potential tree species for ongoing habitat restoration.