白眉长臂猿鸣叫的时间特征

滇西白眉长臂猿(Hylobateshoolock)鸣叫主要发生在上午,最早开始于黎明时分,最晚则在下午16:30以后。平均开始时间为09:05,SD=1095min(N=70,范围07:12～16:30),持续时间为197min,SD=934min(N=55,R=4～50)。多数鸣叫发生在07:00～10:00之间(80%)。不同季节鸣叫发生时间有显著差异,可能与黎明时间(光亮度)不同有关,但持续时间无差异。同一季节异地间鸣叫持续时间差异显著。气候、猿群密度、栖息地状态对鸣叫有一定影响,但未见明显相关性。与黑长臂猿的种间比较表明,白眉长臂猿的鸣叫声在时间分布上有较大的散开度,持续时间也较长,二者有显著差异。     

白眉长臂猿呜叫的时间特征

滇西白眉长臂猿鸣叫主要发生在上午,最早开始于黎明时分,最晚则在下午１６：３０以后,平均开始时间为０９：０５,ＳＤ＝１０９．５ｍｉｎ（Ｎ＝７０,范围０７：１２－１６：３０）,持续时间为１９．７ｍｉｎ,ＳＤ＝９．３４ｍｉｎ（Ｎ＝５５,Ｒ＝４－５０）。多数鸣叫发生在０７：００－１０：００之间（８０％）。不同季节鸣叫发生时间有显著差异,可能与黎明时间（光亮度）不同有关,但持续时间无差异。同一季节异地鸣叫持     

东黑冠长臂猿鸣叫特征及气象因子对鸣叫的影响

鸣叫是长臂猿非常典型的一个特征,并且受到生物因素和非生物因素(如气象因子) 的影响。为了解东黑冠长臂猿的鸣叫特征以及气象因子对鸣叫的影响,2008 年8 月至2009 年10 月,采用全事件记录法对栖息在广西邦亮自然保护区3 个东黑冠长臂猿野生群体的鸣叫行为进行观察。结果表明东黑冠长臂猿倾向于在早晨鸣叫,有91.4% 的鸣叫发生在日出前0.5 h 至日出后3 h 之间,其中53.1% 的鸣叫发生在日出后1 h 内。平均每个群体的鸣叫频次为69.7% ,一个群体平均每天鸣叫1.24 次,鸣叫的平均持续时间为18.3 min。一次二重唱中,雌性平均激动鸣叫4.4 次。长臂猿鸣叫的起始时间在光照强度的影响下差异显著,阴天和雾天鸣叫的起始时间延后,且雾天最迟;降雨致使长臂猿体能的损失和光照强度减弱,从而引起鸣叫起始时间的延后和持续时间缩短;温度对长臂猿鸣叫的影响并不显著。     

黑长臂猿(Hylobates concolor)鸣叫行为研究

本文基于对云南黑长臂猿多年的野外研究,报道其鸣叫行为的一些特性。黑长臂猿通常在上午鸣叫,且大多数发生在930分以前,鸣叫的起始时间具季节性变化,有两个较为集中的时间,一个在730分左右,另一个在830分左右,然而起始时间并不与日出时间一致。黑长臂猿平均每两天鸣叫一次,日鸣叫发生频次在50％左右,鸣叫的发生也随着季节而变化。鸣叫的持续时间无群体的差异,一次鸣叫的平均时间在12分钟左右（除了GG群）,但群体在不同季节鸣叫时间长短不一。本文的研究结果同时还表明一个群体的鸣叫并未引起邻近其它群体的鸣叫。     

西黑冠长臂猿雄性取代前后鸣叫行为的变化

本文通过长时间的野外监测,首次报道了西黑冠长臂猿的一次雄性取代行为。一个研究群体(G3)中的1 只亚成年雄性长臂猿在10 岁左右取代了相邻群体(G2)中的成年雄性。整个取代过程持续了15 d时间。雄性取代发生前,G2 中雌雄的配对关系已经不稳固,这为雄性取代提供了机会。而G2 与G3 群的一次长时间冲突可能消耗了G2 中成年雄性大量体能,这为G3 中的亚成年雄性打败并取代G2 中的成年雄性创造了机会。本研究在取代发生后,对新形成群体的鸣叫行为进行了连续4 个月的监测。结果表明与处于稳定时期的G2 群相比,新形成群体的鸣叫频次更高,但每次二重唱中雌性的平均激动鸣叫次数降低。这证明了Geissmann (1986)提出的假说,新配对的群体应该在尽量短的时间内多练习二重唱,这样导致新配对群体的鸣叫频率明显升高。虽然经历了4 个月的合唱练习,新形成群体的激动鸣叫次数仍然偏低,并且两只雌性同时激动鸣叫的频次也比较低。这说明新形成的配对之间配合依然不默契,或者说明配对之间的关系还不稳定。     

云南高黎贡山赧亢白眉长臂猿春季食谱及活动时间分配初探

从2007年3月9日至4月14日,调查了高黎贡山赧亢的白眉长臂猿的食性和时间分配,旨在为该物种的栖息地保护和食物资源的管理提供指导.观察时,将白眉长臂猿的行为分为取食、移动、休息3种活动类型,利用瞬时扫描取样法取样记录,并记录取食种类及部位.白眉长臂猿春季取食植物种类共有10种,其中果实类植物3种,果汁类植物1种,嫩叶类植物6种.相对其它灵长类而言,其春季的食物多样性较低.白眉长臂猿移动、休息和取食的时间分配分别为33%、35%和32%,较叶猴属动物休息少,移动多.赧亢的白眉长臂猿1天中有3个觅食高峰期,9:00～10:00为第1个觅食高峰;11:00～13:00为第2个觅食高峰;16:00～17:00为第3个觅食高峰.而孟加拉国 Lawachara 的白眉长臂猿仅在早上有两次觅食高峰.这种差异可能是不同区域的白眉长臂猿对环境的适应结果.     

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。     

无量山西黑冠长臂猿二重唱的声谱结构和时间特征

2003年3月—2004年3月对无量山大寨子3群西黑冠长臂猿的二重唱的时间特征进行了监测。于2007年3月和2008年3月利用Sony TC-D5 Pro2录音机、Sony C-76指向性话筒和Sony录音磁带对其二重唱进行了录音,对录音效果最好的5个声音用Signal/RTS 4.0软件进行声谱分析。对无量山西黑冠长臂猿二重唱的声谱结构和时间特征的研究结果表明,雄性西黑冠长臂猿的声音由起始音节、简单的重复音节和调节音节组成。根据频率变化的强度,可以将调节音节分为弱调节音节和强调节音节。强调节音节的特征是第二个音节具有非常明显的频率变化,有时第三个音节有类似变化,变频时的最高频率可达到5 828 Hz。雌性长臂猿一般只会发出一种类型的声音,即固定而刻板的激动鸣叫。根据激动鸣叫是否完整可以分为成功的激动鸣叫和失败的激动鸣叫。典型的西黑冠长臂猿二重唱通常由成年雄性发起,并占主导地位,且一般由雄性结束。雌性激动鸣叫结束后,雄性马上发出调节音节与之配合,雄性调节音节与雌性激动鸣叫的时间间隔平均为2.7 s。平均每个群体的鸣叫频次为53%。如果发生鸣叫,一个群体平均每天鸣叫1.09次。91.5%的鸣叫发生在日出前0.5 h至日出后3 h之间,其中48.6%的鸣叫发生在日出后1 h内。在一次鸣叫中,雌性平均发出成功的激动鸣叫4.6次,两次成功的激动鸣叫之间的时间间隔平均为115 s。群体间均未显示鸣叫频次和持续时间上的差异,但激动鸣叫次数和激动鸣叫时间间隔具有显著差异。     

高黎贡山大塘白眉长臂猿春季栖息地利用

2007年3月9日～4月6日,在高黎贡山自然保护区大塘片区调查白眉长臂猿生境利用行为.设置利用和可利用样地各30个.对定性因子的检验和Bonferroni置信区间分析表明,大塘片区白眉长臂猿偏爱在东坡 (阳坡) 和中下坡位活动.定量因子分析表明,利用和可利用样地中共有5个因子存在显著差异 (坡度、距水源距离、距道路距离、灌木平均高度和藤本密度).回归检验结果显示,坡度和藤本密度为影响大塘片区白眉长臂猿生境利用的主要因子.大塘片区白眉长臂猿对地理空间的选择反应了避风和趋向阳光的需求.在大塘,白眉长臂猿适宜栖息的植被有较高的均匀性.白眉长臂猿对高大乔木具有依赖性和选择偏好,对林下竹灌层的选择不高与植被分布均匀和人为干扰强度较小有关.藤本植物是白眉长臂猿在乔灌层之间活动的主要交通媒介和连接纽带.     

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.     

Sound Spectrum Characteristics of Songs of Hainan Gibbon (Nomascus hainanus)

Gibbons are characterized by their species-specific calls, or songs. There are few studies of songs of Hainan gibbon (Nomascus hainanus). To study the sound spectrum characteristics and test for intergroup differences in Hainan gibbon song, we studied the singing behavior of Hainan gibbons in Bawangling National Nature Reserve, Hainan Province, China, intermittently from August 2002 to February 2013, collecting 184 recordings. Our results show that: 1) Hainan gibbon song bouts occur mainly 0–4 h after dawn. 2) The songs of adult males living in groups are composed mainly of one to three short notes and one to five long notes, while solitary adult male songs consist only of long frequency modulated notes and no short or single notes. 3) The song chorus is dominated by adult males, while females add a great call. Males do not have a great call, unlike those in other gibbon species. There are no female solos. 4) The sound spectrum frequency is similar in adult males living in two different groups, but the duration of the first long note differed significantly between the groups. The sonic frequencies of male and female songs are lower than those of other gibbons: no more than 2 kHz. Hainan gibbon sound structure is simple, although females participate in the chorus, reflecting their primitive status among gibbon species.     

Detection of a New Hainan Gibbon (<Emphasis Type="Italic">Nomascus hainanus</Emphasis>) Group Using Acoustic Call Playback

Targeted management actions informed by robust data are needed to conserve species of extreme rarity, and assessing the effectiveness of different field methods for detection and monitoring of such species is a conservation priority. Gibbons are typically detected by their daily song through passive listening surveys, but lone gibbon individuals and low-density populations are less likely to sing, making detection difficult or impossible using standard survey techniques. Call playback represents an alternative potential method for detecting gibbon presence, but there has been no empirical evaluation of the usefulness of this method in the field. We investigated the efficacy of call playback as a survey method for detecting previously unconfirmed or unknown individuals of the Critically Endangered Hainan gibbon (Nomascus hainanus), the world’s rarest primate, in patches of good-quality forest outside the current home ranges of the three known Hainan gibbon social groups in Bawangling National Nature Reserve, Hainan, China. Call playback led to detection of a male-only call likely to have been made by a solitary male, and a previously unknown social group comprising an adult male, adult female, and an infant, increasing the number of known breeding females in the global Hainan gibbon population from five to six. Call playback therefore represents an effective tool for improved monitoring of Hainan gibbons, as well as other gibbon populations; however, it is a moderately disruptive survey technique, and should be employed sparingly, in key locations, and for short periods of time only when attempting to detect gibbon presence.     

Selection of Fruit by Gibbons (Hylobates muelleri × agilis) in the Rain Forests of Central Borneo

Gibbons (Hylobates spp.) are among the main frugivorous primates in Southeast Asia, yet little is known about the criteria by which they select fruit for consumption. We studied two gibbon groups for 14 mo in the lowland dipterocarp forests of Central Borneo to determine their selectivity for different fruit species and traits. Ideal gibbon fruit were yellow, large, with a juicy-soft pulp, thin skin and available in large crops. Gibbons ultimately sought seedless fruit, but when seeds were present they selected fruit with a single, well-protected seed. Given that few fruit exhibited all the desired traits, we also carried out a multiple regression using the selection ratios of the various fruit species and their associated fruit traits to determine which traits ultimately determined gibbon choice. The analysis was stratified to account for differences in fruit availability. Selection was strongest when fruit were abundant in the forest and was based on seed width (<21 mm), color (yellow-orange), and fruit weight (1–5 g). No selection is apparent when food abundance was intermediate, but when fruit were scarce they preferentially ate larger fruit (6–30 g).     

Behavioral responses of Cao Vit gibbon (Nomascus nasutus) to variations in food abundance and temperature in Bangliang, Jingxi, China

The Cao Vit gibbon is a critically endangered species with only about 110 individuals remaining in a degraded karst forest along the China-Vietnam border. Behavioral data from this site are particularly useful in understanding gibbon behavioral adaptations to different sets of ecological conditions and will contribute to the conservation of the species. We studied seasonal variation in the time budget and diet of the Cao Vit gibbon in response to variation in food availability and ambient temperature by observing two groups for 1,379 hr between January and December 2009. We used 5-min scan samples to record the activity of gibbons. Both ambient temperature and food availability varied from month to month. Gibbon groups increased resting time and huddled together in sleeping places in cold months. Gibbons spent more time feeding on fruit when fruit was more abundant suggesting that fruit was their preferred food. Alternatively, leaf eating was negatively correlated with leaf availability which suggested that leaves may be used as a fallback food. Gibbons increased their diet diversity when they ate more leaves. This might be a strategy to cope with toxins or digestion inhibitor accumulation associated with feeding from a limited number of leaf species. Individuals consumed more buds when Broussonetia papyrifera produced buds in March and April. During this period, they decreased traveling time and engaged in less frequent social interactions. Gibbons spent more time searching for and feeding on invertebrates during June and October. However, we did not collect data on invertebrate abundance and therefore cannot determine the relationship between invertebrate feeding and availability. We conclude that flexibility in consuming diverse food types and food species, and in responding to the availability of preferred foods, has enabled the Cao Vit gibbon to survive in a degraded karst forest habitat.     

Status and distribution pattern of black crested gibbon (Nomascus concolor jingdongensis) in Wuliang Mountains, Yunnan, China: implication for conservation

The western black crested gibbon (Nomascus concolor), or black gibbon, one of the lesser apes (Hylobatidae), is mainly distributed in Yunnan, China. Of the four recognized subspecies, N. c. jingdongensis is endemic to the Wuliang Mountain, central Yunnan, China. Of all the subspecies, this one has the largest population of any black gibbon. However, the data were all based on brief estimates. We carried out an extensive field survey on population and group distribution of the black gibbon in the Wuliang Mountains by use of loud morning songs and interviews with local people. Ninety-eight groups were confirmed and located in the mid-montane range of Wuliang Mountains. More groups are found on the east slope and the southern region than in the west and the north. Gibbons are more disjunctly distributed on the west slope, especially in the northern part. Deforestation in the late 1950s, 1960s and 1970s was the main reason for rapid loss of habitat and population decline. Hunting was another key reason for population decline and, in many cases, the main reason for local extinction.     

Sleeping Tree Selection of Cao Vit Gibbon (Nomascus nasutus) Living in Degraded Karst Forest in Bangliang,Jingxi, China

We studied the sleep‐related behavior of two Cao Vit gibbon (Nomascus nasutus) groups in Bangliang Nature Reserve in Jingxi County, China between January 2008 and December 2009 to test four hypotheses related to sleeping tree selection (predation avoidance, thermoregulation, food access, and range defense). Gibbons entered sleeping trees 88 ± SD 37 min before sunset before their main potential nocturnal predator become active. They usually moved rapidly and straight to sleeping trees and kept silent once settled. Over the course of the study, gibbon groups used many (87 and 57 per group) sleeping trees and reused them irregularly. They also tended to sleep in relatively tall trees without lianas, choosing small branches close to the treetop. These behaviors would make it difficult for potential terrestrial predators to detect and approach the gibbons. Therefore, these results strongly support the predation avoidance hypothesis. Gibbons tended to sleep closer to ridges than to valley bottoms and they did not sleep at lower elevations in colder months. They thus appeared not to select sleeping trees to minimize thermoregulatory stress. Gibbons very rarely slept in feeding trees, instead generally sleeping more than 100 m away from the last feeding trees of the day or the first feeding tree of the next morning. These patterns led us to reject the food access hypothesis. Lastly, we did not find evidence to support the range defense hypothesis because gibbons did not sleep in overlap areas with neighbors more often than expected based on the proportion of overlap and exclusively used areas. Am. J. Primatol. 74:998‐1005, 2012. © 2012 Wiley Periodicals, Inc.     

Group size and stability: Why do gibbons and spider monkeys differ?

Gibbons and spider monkeys have similar diets, body size, and locomotor patterns. They are therefore expected to be subject to similar socioecological rules. However their grouping patterns differ. Gibbons live in small stable groups, whereas spider monkey form unstable sub-groups that vary from small to large during different seasons. If similar principles apply to the two species, food abundance should vary more for spider monkeys than for gibbons; food density should be similar for the two species when spider monkey sub-groups are the same size as gibbon groups; and the highest level of food abundance should be higher for spider monkeys than for gibbons. These predictions are upheld for a comparison of particular populations ofHylobates muelleri andAteles geoffroyi.     

Cues to Androgens and Quality in Male Gibbon Songs

Animal vocal signals may provide information about senders and mediate important social interactions like sexual competition, territory maintenance and mate selection. Hence, it is important to understand whether vocal signals provide accurate information about animal attributes or status. Gibbons are non-human primates that produce loud, distinctive and melodious vocalizations resembling more those of birds than of other non-human primates. Wild gibbons are characterized by flexibility in social organization (i.e., pairs and multimale units) as well as in mating system (i.e., monogamy and polyandry). Such features make them a suitable model to investigate whether the physiology (hormonal status) and socio-demographic features find their correspondence in the structure of their songs. By combining male solo song recordings, endocrine outputs using non-invasive fecal androgen measures and behavioral observations, we studied 14 groups (10 pair-living, 4 multimale) of wild white-handed gibbons (Hylobates lar) residing at Khao Yai National Park, Thailand. We collected a total of 322 fecal samples and recorded 48 songs from 18 adult animals. Our results confirmed inter-individuality in male gibbon songs, and showed a clear correlation between androgen levels and song structures. Gibbons with higher androgen levels produced calls having higher pitch, and similarly adult individuals produced longer calls than senior males. Thus, it is plausible that gibbon vocalizations provide receivers with information about singers'' attributes.