Wang Yuan, Lv Yonglei, Wang Guanglong, Liu Feng, Ji Yingxun, Liu Zheng, Zhao Wanglin, Liu Wulin, Dun Zhu Pu Bu, Jin Kun
Ecology and Nature Conservation Institute, Chinese Academy of Forestry, Beijing 100091, China.
Tibet Autonomous Region Research Institute of Forestry Inventory and Planning, Lhasa 850000, China.
Animals (Basel). 2024 Aug 21;14(16):2426. doi: 10.3390/ani14162426.
Limited background data are available on the Mishmi takin () and Bhutan takin () subspecies in the Eastern Himalayas of China because of the lack of systematic field investigations and research. Therefore, mature-animal ecological methods were used to evaluate these takin subspecies' phenotypic characteristics, distribution range, activity rhythm, and population size. From 2013 to 2022, 214 camera traps were installed for wild ungulate monitoring and investigation in all human-accessible areas of the Eastern Himalayas, resulting in 4837 distinguishable takin photographs. The external morphological characteristics were described and compared using visual data. Artificial image correction and related technologies were used to establish physical image models based on the differences between subspecies. MaxEnt niche and random encounter models obtained distribution ranges and population densities. Mishmi takins have a distribution area of 17,314 km, population density of 0.1729 ± 0.0134 takins/km, and population size of 2995 ± 232. Bhutan takins have a distribution area of 25,006 km, population density of 0.1359 ± 0.0264 takins/km, and population size of 3398 ± 660. Long-term monitoring data confirmed that the vertical migration within the mountain ecosystems is influenced by climate. Mishmi takins are active at 500-4500 m, whereas Bhutan takins are active at 1500-4500 m. The two subspecies were active at >3500 m from May to October yearly (rainy season). In addition, surveying combined with model simulation shows that the Yarlung Zangbo River is not an obstacle to migration. This study provides basic data that contribute to animal diversity knowledge in biodiversity hotspots of the Eastern Himalayas and detailed information and references for species identification, distribution range, and population characteristics.
由于缺乏系统的野外调查和研究,关于中国东喜马拉雅地区米什米羚牛()和不丹羚牛()亚种的背景数据有限。因此,采用成熟动物生态方法来评估这些羚牛亚种的表型特征、分布范围、活动节律和种群数量。2013年至2022年期间,在中国东喜马拉雅地区所有人类可进入的区域安装了214台相机陷阱,用于监测和调查野生有蹄类动物,共获得4837张可识别的羚牛照片。利用视觉数据描述并比较了其外部形态特征。基于亚种间的差异,运用人工图像校正及相关技术建立了物理图像模型。通过最大熵生态位模型和随机相遇模型得出分布范围和种群密度。米什米羚牛的分布面积为17314平方公里,种群密度为每平方公里0.1729±0.0134头,种群数量为2995±232头。不丹羚牛的分布面积为25006平方公里,种群密度为每平方公里0.1359±0.0264头,种群数量为3398±660头。长期监测数据证实,山地生态系统内的垂直迁移受气候影响。米什米羚牛在海拔500 - 4500米处活动,而不丹羚牛在海拔1500 - 4500米处活动。这两个亚种每年5月至10月(雨季)在海拔>3500米处活动。此外,调查结合模型模拟表明,雅鲁藏布江不是迁移障碍。本研究提供了有助于了解东喜马拉雅生物多样性热点地区动物多样性的基础数据,以及物种识别、分布范围和种群特征的详细信息和参考依据。