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。     

无量山大寨子黑长臂猿(Nomascus concolor jingdongensis)种群生存力

据2003年9月至2005年9月,对云南中部无量山大寨子黑长臂猿种群(5个群体)进行了观察,获得了群体大小、配偶体制、繁殖间隔、环境容纳量、死亡率、灾害的发生频率等种群参数,并结合近缘种的一些相关数据,利用旋涡模型(Vortex 914),对无量山大寨子地区黑长臂猿亚种群的动态进行了模拟分析。结果显示:大寨子亚种群是一个具有很强的潜在繁殖力的种群,如果没有偷猎,亚种群在100a之内不会灭绝,并且能迅速达到环境容纳量。但是每年如果有1只成年雄性和1只成年雌性被猎杀,该种群将会在第78年灭绝,且灭绝概率为100%。不同程度的死亡率对种群影响不大,但高死亡率显著延缓了种群到达环境容纳量的时间。环境容纳量对种群遗传多样性损失具有重要的影响,在没有猎杀的情况下,种群的长期存活需要一个较大的环境容纳量。因此,在黑长臂猿受到严格保护、且栖息地主要在保护区内的今天,严密监控火灾的发生,限制牲畜进入林区等人为干扰的影响,保护好黑长臂猿栖息地是首要工作之一。但如果能使其栖息地周围的森林植被得到恢复,增加其栖息范围,将有利于该地区黑长臂猿的发展。     

无量山大寨子黑长臂猿(Nomascus concolor jingdongensis)种群生存力

据2003年9月至2005年9月,对云南中部无量山大寨子黑长臂猿种群（5个群体）进行了观察,获得了群体大小、配偶体制、繁殖间隔、环境容纳量、死亡率、灾害的发生频率等种群参数,并结合近缘种的一些相关数据,利用旋涡模型（Vortex 914）,对无量山大寨子地区黑长臂猿亚种群的动态进行了模拟分析。结果显示：大寨子亚种群是一个具有很强的潜在繁殖力的种群,如果没有偷猎,亚种群在100a之内不会灭绝,并且能迅速达到环境容纳量。但是每年如果有1只成年雄性和1只成年雌性被猎杀,该种群将会在第78年灭绝,且灭绝概率为100%。不同程度的死亡率对种群影响不大,但高死亡率显著延缓了种群到达环境容纳量的时间。环境容纳量对种群遗传多样性损失具有重要的影响,在没有猎杀的情况下,种群的长期存活需要一个较大的环境容纳量。因此,在黑长臂猿受到严格保护、且栖息地主要在保护区内的今天,严密监控火灾的发生,限制牲畜进入林区等人为干扰的影响,保护好黑长臂猿栖息地是首要工作之一。但如果能使其栖息地周围的森林植被得到恢复,增加其栖息范围,将有利于该地区黑长臂猿的发展。     

无量山大寨子黑长臂猿（Nomascus concolor fingdongensis）种群生存力

据2003年9月至2005年9月,对云南中部无量山大寨子黑长臂猿种群（5个群体）进行了观察,获得了群体大小、配偶体制、繁殖间隔、环境容纳量、死亡率、灾害的发生频率等种群参数,并结合近缘种的一些相关数据,利用旋涡模型（Vortex 914）,对无量山大寨子地区黑长臂猿亚种群的动态进行了模拟分析。结果显示：大寨子亚种群是一个具有很强的潜在繁殖力的种群,如果没有偷猎,亚种群在100a之内不会灭绝,并且能迅速达到环境容纳量。但是每年如果有1只成年雄性和1只成年雌性被猎杀,该种群将会在第78年灭绝,且灭绝概率为100％。不同程度的死亡率对种群影响不大,但高死亡率显著延缓了种群到达环境容纳量的时间。环境容纳量对种群遗传多样性损失具有重要的影响,在没有猎杀的情况下,种群的长期存活需要一个较大的环境容纳量。因此,在黑长臂猿受到严格保护、且栖息地主要在保护区内的今天,严密监控火灾的发生,限制牲畜进入林区等人为干扰的影响,保护好黑长臂猿栖息地是首要工作之一。但如果能使其栖息地周围的森林植被得到恢复,增加其栖息范围,将有利于该地区黑长臂猿的发展。     

海南长臂猿的家族群相遇行为观察

海南长臂猿(Nomascus hainanus)是野外研究最少的长臂猿种类之一。在过去的十多年中,只了解其种群数量、种群结构、栖息地和有关于其食物种类的极少量信息。对于世界上最濒危的灵长类之一的海南长臂猿,在长达4年的野外研究中,主要采用扫描取样法和焦点动物取样法观察到了4次海南长臂猿的合群现象,并发现了现存的两群海南长臂猿之间的合群行为不同于其他长臂猿,如白掌长臂猿(Hylobates lar)的合群行为。在海南长臂猿的合群行为中,只观察到了雌雄性成年个体和雄性亚成体以及青年雄性个体之间的鸣叫和追逐行为,而没有发现像白掌长臂猿样的两群体成员间的玩耍和理毛行为,更没有偷情行为和白掌长臂猿那样致命的激烈打斗行为的存在,即只存在着鸣叫行为和竞争性行为。两群体的雌性成年母猿根本就不参与到追逐行为中,它们只是在相距合群行为发生地点20—30m处休息和观望。同时,海南长臂猿相遇的持续时间也不像其他种类的长臂猿那样长,只有24—51min。另外,也没有发生打斗行为。对于海南长臂猿雌雄性成年个体在群体相遇时的行为,我们认为是它们对其领域的保护,而未成年个体则是通过参与这种追逐方式学习如何保护自己今后的领域。     

以长臂猿为荣

正"全球范围内,目前仅发现中国云南盈江县境内的傈僳族居民与东白眉长臂猿这一物种特别友好。虽然这个民族是个公认的捕猎高手,可他们的祖先为其留下一个非常难能可贵的传统习俗,就是不许猎杀长臂猿。这个民族认为白眉长臂猿是神猴,这种习俗在全中国乃至全球分布有长臂猿的地方是独一无二的。"FFI中国灵长类项目负责人蒙秉波说,"一个地方的保护物种种群数量能不能增长,和偷猎盗采情     

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。     

海南长臂猿线粒体D-loop区序列分析及种群复壮

海南长臂猿(Nomascus hainanus)是世界上最濒危的灵长类动物之一, 但目前有关海南长臂猿的种群遗传学方面的信息以及种群复壮所面临的困难未见报道。为更好地保护该极危物种, 作者以粪便为研究材料, 首次在分子生物学水平上测定了海南长臂猿1个群体(B群)共6个个体的线粒体D-loop区基因序列。结果显示: 202 bp的D-loop区基因共检测到5个变异位点, 4个单倍型, 单倍型多样性(h)为0.6000, 核苷酸多样性(π)为0.00829, 表明海南长臂猿B群的遗传多样性较低; 与此同时, 海南长臂猿还面临着种群数量过小, 性比失衡, 以及栖息地质量低下等严峻的问题。     

群体大小和觅食环境变化对东黑冠长臂猿日移动距离的影响

日移动距离是反映动物觅食努力的重要指标之一,相关研究有助于了解动物对生境的适应策略,对濒危物种的保护至关重要.东黑冠长臂猿(Nomascus nasutus)是一种极度濒危的树栖小型类人猿,主要生活在一夫二妻制的群体中,平均群体大小6.3只,目前对于该物种的日移动距离仍然缺乏足够的科学研究.我们以广西邦亮长臂猿国家级自...     

野生大熊猫现状、面临的挑战及展望

截至2003年底,我国野生大熊猫种群数量达1596只,分布在陕西、四川和甘肃3省的45个县境内,总栖息地面积达2304991hm^2。与第2次大熊猫调查相比,野生大熊猫生存状况已得到改善,分布范围扩大、栖息地面积增加、种群数量进一步增长。本文在第3次大熊猫调查的基础上,就野生大熊猫种群及栖息地现状进行了分析,指出未来保护大熊猫所面临的3个方面的挑战,即来自物种自身生物学特性的挑战、栖息地破碎化及隔离小种群未来命运的挑战以及大熊猫保护与社区经济发展需求相冲突的挑战。作者还就我国大熊猫保护前景进行了展望,即自然保护区数量将进一步增加,栖息地状况将进一步改善;种群数量在总体保持稳定的基础上将逐步增长,但局部小种群灭绝风险将加剧;圈养种群将形成能自我维持的种群,圈养个体通过培训将逐步放归到隔离野生小种群中以改变其命运。     

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。     

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.     

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.     

The yellow-cheeked gibbon (Hylobates gabriellae) in nam bai cat tien (southern vietnam) revisited

Data concerning the status, habitat, and vocalizations of yellow-cheeked crested gibbons (Hylobates gabriellae) were collected during a short field trip to the Nam Bai Cat Tien National Park (southern Vietnam). Nam Bai Cat Tien may be the southernmost locality where crested gibbons (i.e. theHylobates concolor group) still survive. Fewer songs were heard at Nam Bai Cat Tien National Park than at other crested gibbon sites visited by the author. At least two gibbon groups appear to have been greatly reduced in number since previous surveys in the park. There is some evidence that both the gibbon population and the gibbon habitat in Nam Bai Cat Tien are disturbed. The first case of a great call solo song in wild gibbons of theconcolor group is reported. Great calls ofH. gabriellae are described and documented with sonagrams for the first time. They differ from those previously described forH. leucogenys.     

Social structure and group dynamics of the Cao Vit gibbon (Nomascus nasutus) in Bangliang, Jingxi, China

The Cao Vit gibbon (Nomascus nasutus) was rediscovered in 2002 in Vietnam and then in 2006 in China. This is the only known population with about 110 individuals located along the China-Vietnam border. Little is known about it other than its population size and distribution. We describe the social structure and group dynamics of the Cao Vit gibbons in China based on 2 years of monitoring from 2007 to 2009. Four established study groups at this site consisted of 1 adult male, 2 adult females and 2-6 offspring. Two juveniles in 2 groups disappeared during the research. Four infants were born in 3 groups from November 2008 to February 2009. In 2 of the groups, both adult females had dependent infants. These observations suggest that Cao Vit gibbons live in polygynous groups, contrary to the usual monogamous group with only 1 adult female, but nevertheless similar to the social organization of both N. concolor and N. hainanus. We observed a coordinated dispersal of 1 adult male and 2 large juveniles, and the male formed a pair with a newly arrived female. Our observations support a growing awareness of variability in gibbon social organization.     

Predation on giant flying squirrels (Petaurista philippensis) by black crested gibbons (Nomascus concolor jingdongensis) at Mt. Wuliang, Yunnan, China

Predation on vertebrates is infrequent in gibbons. In a 14-month field study of the central Yunnan black crested gibbon (Nomascus concolor jingdongensis) at Mt. Wuliang, Yunnan, China, we observed gibbons attacking, killing and eating giant flying squirrels (Petaurista philippensis). During 845 h of observation on one study group, the gibbons attacked giant flying squirrels 11 times, and succeeded in 4 cases. Although all members of the group attempted to attack the squirrels, all four successful attacks were made by the same adult female. The victims were infants in three cases and a juvenile or sub-adult in one case. Black crested gibbons also attacked adult giant flying squirrels by grabbing their long tails and throwing them from the canopy, but they failed to catch or kill the prey in three cases observed. Passive meat sharing occurred in three out of four successful cases. Besides hunting giant flying squirrels, the black crested gibbons also ate eggs or chicks in two birds’ nests and one lizard.