灵长类家域的研究

灵长类家域的研究李保国刘安宏（西北大学生物学系,西安７１００６９）（西安市林业局,７１０００３）ＨｏｍｅＲａｎｇｅＳｔｕｄｙｏｆＰｒｉｍａｔｅｓ．￥ＬｉＢａｏｇｕｏ（ＤｅｐａｒｔｍｅｎｔｏｆＢｉｏｌｇｙ,ＮｏｒｔｈｗｅｓｔＵｎｉｖｅｒｓｉｔｙ,Ｘｉａ...     

Divergent movement patterns of adult and juvenile ‘Akohekohe,an endangered Hawaiian Honeycreeper

The movement patterns of birds across a landscape are often highly variable and influenced by complex interactions between individuals and environments. Because periods of movement can be marked by high mortality, especially among juvenile birds, understanding these patterns may be vital for the conservation of many bird species. However, these patterns can be challenging to quantify. We used radio-telemetry to document the movement patterns of ‘Akohekohe (Palmeria dolei), an endangered Hawaiian Honeycreeper endemic to Maui Island, Hawai'i. This species is believed to be highly susceptible to mosquito-transmitted avian malaria (Plasmodium relictum) and only breeds in high-elevation wet forests on the windward side of east Maui (> 1715 m) that serve as mosquito-free refugia. Over a 2-yr period (2013–2014), we used radio-telemetry and resightings of color-banded birds to track the movements of juveniles (N = 11) and adults (N = 24) and quantified home ranges with minimum convex polygons (MCP) and 95% fixed kernels (KHR). Movement patterns and home range sizes of adult and juvenile ‘Akohekohe were significantly different, with adults having relatively small home ranges (0.57 ha, MCP; 1.09 ha, KHR) and juveniles moving greater distances and having larger home ranges (25.02 ha, MCP; 90.56 ha, KHR). Only juveniles moved into lower-elevation forests that can support mosquito populations, at least seasonally. The absence of adults in this transitional malaria zone suggests that adult ‘Akohekohe cannot maintain long-term home ranges in areas with an increased risk of malaria infection. In addition, the long-distance movements of juveniles during the post-fledging, pre-breeding period likely increases their risk of contracting avian malaria and could be a key factor limiting the population of this species.     

Status and ecology of the golden monkey (Cercopithecus mitis kandti) in Mgahinga Gorilla National Park, Uganda

Given the degree to which tropical ecosystems are currently being disturbed by human activities, it is essential to set priorities for conservation and thus it becomes important to consider how best to set these priorities. From this perspective, this study provides the first detailed investigations of Cercopithecus mitis kandti, the golden monkey, focusing on the population in Mgahinga Gorilla National Park (MGNP), Uganda. Specifically, we (1) establish the current status of the golden monkey in terms of population size and distribution within the park in relation to vegetation types and altitude, and (2) investigate the golden monkey's feeding ecology. A total of 67 censuses of 4+ km transects were conducted along a cumulative distance of 299 km and 132 social groups were encountered. Densities were estimated to have increased by 1.6 times since a census 8 years ago, and the total population in the park is estimated to be between 3164 and 5059 individuals. The average size of golden monkey groups in MGNP is 30 individuals (range 3–62). This is similar to that of other subspecies in neighbouring forests. In contrast, the census conducted 8 years before estimated average group size to be eight individuals. Golden monkeys were observed to eat 21 plant species and they were inferred to eat an additional eleven from signs left behind and reports. Both study groups relied upon leaves (primarily young leaves), fruits and invertebrates for food, but the amount of time they fed on these different types of foods varied between the groups. Given the apparent increase in density since the census 8 years ago, the golden monkeys of MGNP appear to be doing well. However, given the number of snares and the extent of illegal extraction of bamboo found during the census, conservation efforts should be increased.     

Mangabey (Cercocebus albigena) population density,group size,and ranging: A twenty-year comparison

Mangabey groups studied in the Kibale Forest Reserve, Uganda, in 1971 were studied again in 1991 using similar data collection protocols. The results were used to assess the effect of group size on activity budgets and travel costs, and to document the effects of habitat changes on mangabey density and demography. Larger mangabey groups traveled longer distances per day than smaller groups. Time budgets were less clearly influenced by group size. Mangabey population density increased over the 20 year period. This increase in population density paralleled habitat changes, particularly an increase in tree density, and was accompanied by increased use of regenerating forest. © 1994 Wiley-Liss, Inc.     

Home range, home range overlap, and species energy use among herbivorous mammals

Harestad & Bunnell (1979) showed that, at least for North American species, home ranges of large herbivorous mammals are relatively larger than we would expect on metabolic grounds, and suggested that the productivity of the environment for mammal species decreases with increasing body size. This interpretation assumes that the number of conspecifics that share an individual's home range is independent of body size. Data presented here show that this is not true for the species in their sample; the home range is shared with an increasing number of conspecifics in larger herbivore species. The productivity of the environment for a species is independent of body size and the area available to an individual for its own use scales approximately as do individual metabolic requirements. These results agree with conclusions based upon the scaling of population density with body mass and illustrate the interrelationship between home range and dietary and social organization trends among mammalian herbivores. Individual home range area is a function of the way in which the local population of a species, not merely an individual, exploits the environment.     

Twenty-four hours in the life of Zingel asper

For the first time, radio-tracking observations were made over 24 h cycles during the growing season to quantify the habitat use and home range of Zingel asper , a critically endangered fish species, endemic to the Rhône River with a high risk of extinction (IUCN). New advances in radio telemetry with regard to the size of tags provided an opportunity to collect behavioural and habitat use information while remaining non-lethal. Zingel asper was characterized by small ranges of habitat use and, contrary to previous assumptions, the species was diurnal as illustrated by a smaller home range during the night than during daytime.     

Effects of Group Size on Ranging Patterns in Brachyteles arachnoides hypoxanthus

We collected systematic data on the home range and day ranges of one group of 57–63 muriquis (Brachyteles arachnoides hypoxanthus) at the Estação Biológica de Caratinga, Minas Gerais, Brazil from September 1998–July 1999, and compared them with similar data collected 15 years ago when the 23–27 individuals in the group traveled together as a cohesive unit. Home range size increased from 168 ha to 309 ha, reflecting an expansion into areas of the forest that were previously unutilized and consistent with the positive relationship predicted between group size and home range size. By contrast, muriquis exhibited remarkable seasonal and interannual stability in their day ranges. Day ranges, which were calculated from 144 days with 8 h of observation, averaged 1,313 ± 573 m (median = 1,206 m). Day ranges did not vary with the size of subgroups, defined as independent individuals that traveled with one another out of contact with other group members. Subgroups were significantly larger during the rainy season (mean = 41.8 ± 12.7, median = 46.0 individuals, n = 72) than the dry season (mean = 36.6 ± 13.25, median = 39.5 individuals, n = 72). Subgroups were also larger than the size of the entire group during the previous study, yet their day ranges are indistinguishable. The stability in muriqui day ranges is consistent with predictions for folivorous primates in which other indicators of intragroup feeding competition, such as female dominance relationships, are also absent. We attribute the transition from cohesive to fluid grouping patterns to limits on the number of individuals that can coordinate their movements when they spread out while foraging and suggest that seasonal differences in subgroup sizes without corresponding adjustments in day ranges reflect seasonal differences in the distribution of preferred foods coupled with the effects of reproductive seasonality on muriqui grouping patterns.     

Group Size, Home Range Use, and Seasonal Variation in the Ecology of Eulemur mongoz

We collected data during a 10-month study carried out on the mongoose lemur, Eulemur mongoz, at Anjamena in northwestern Madagascar, which provide baseline information on seasonal variation in the ecology, home range use and some aspects of the behavior of two neighboring groups. We monitored group size of nine groups in the study area and assessed them for seasonal variation. We present additional information collected during short-term surveys in other areas before and during the study for comparison. The study groups were small family units, and changes in group size were limited to births and emigrations of sexually mature progeny. In spite of clear seasonal changes in climate and vegetation, there is no variation in grouping patterns, so it is not possible to correlate variation in group size with seasonal variation of ecological variables. Comparison with ecological data from other field studies on lemurids reveals differences in food resource distribution in western forests versus other types of Malagasy forest. This distribution of food resources may predict home range size in mixed frugivorous–folivorous lemurs. Small home ranges, mainly in the West, could be correlated with a uniform distribution of food resources. Finally, we suggest that the dry season in the West may not present frugivorous–folivorous lemurs with major problems in finding an adequate food supply. This is supported by the lack of seasonal differences in ranging behavior of mongoose lemurs.     

生态系统受威胁等级的评估标准和方法

生态系统受威胁等级评估是认识生物多样性丧失的重要手段.在2008年的第四次世界自然保护大会上,国际自然保护联盟(IUCN)成立专门工作组,着手建立类似于物种灭绝风险的定量评估方法,对生态系统受威胁等级进行评估.最终的目标是在局地、区域和全球尺度上确定生态系统的受威胁等级,建立生态系统红色名录.在制定生物多样性保护策略时,生态系统红色名录与物种红色名录可作为互补.目前,生态系统受威胁等级评估方案的评估依据包括4类:生态系统分布或生态系统功能短期衰退;生态系统分布或生态系统功能长期衰退;生态系统当前的分布狭窄、同时生态系统分布或生态系统功能衰退;生态系统当前的分布极狭窄.应用Rodríguez等(2011)建立的评估标准,基于文献记载的中国辽河三角洲4个生态系统1988年和2006年的面积,我们详细介绍了生态系统受威胁等级的评估过程.目前的评估方法面临挑战,生态系统分布范围和占有面积的估计应基于合理的空间尺度,同时还需建立合理的方法定量描述生态系统功能的变化.生态系统受威胁等级评估方案将提交2012年召开的世界自然保护大会讨论.     

Primate Population Densities and Sizes in Atlantic Forest Remnants of Northern Espírito Santo,Brazil

We surveyed primates in seven fragments of Atlantic forest ranging from 210 to 24,250 ha in Espírito Santo, southeastern Brazil. The objective was to assess their population densities and fragment-specific population sizes in order to discuss the survival of primates in this highly fragmented landscape. We used line-transect sampling for censusing primates and estimated densities via DISTANCE program. Alouatta fusca, Cebus apella, Callicebus personatus, and Callithrix geoffroyi live in the study area. Although variable, primate numbers were higher in larger than in smaller fragments, the likely reasons being the lack of space and food resources (fruits) and higher impact of mesopredators (small cats) in small fragments. The estimated densities are within the range reported for other Atlantic forest sites, except for brown howlers (Alouatta fusca), which were extremely rare. Estimates of population sizes were on the order of several hundreds to thousands of individuals/species in the large-sized fragments (ca. 20,000 ha), while comparable estimates for the other areas indicate <500 individuals/species in the medium-sized reserves (ca. 2,000 ha), and <50 individuals/species in the small fragments (ca. 200 ha). These estimates suggest that only Atlantic forest fragments 20,000 ha can harbor primate populations large enough to escape extinction in the long term. Given that <20% of all protected areas remaining in the Atlantic forest are 20,000 ha, management measures are urgently needed to improve primate conservation in this biome.