Tigers at higher elevations outside their range: What does it mean for conservation?

Pub Date : 2021-01-01 DOI:10.1553/eco.mont-14-1s43
S. Shrestha, A. Sherpa, Sony Lama, Munmun Tamang, P. Paudel
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Even though high-altitude ecology may be suitable for tiger growth, the formulation of a high-altitude tiger conservation action plan with effective coordination between stakeholder organizations and concerned departments is of great importance. Tigers are an apex species of the terrestrial ecosystem and exist in a precarious state throughout their range. The tiger is a globally endangered species (Goodrich et al. 2015). In the past, the tiger once existed as nine subspecies, now reduced to only six subspecies that exist in the wild. The subspecies Bengal tiger (Panthera tigris) has the largest population and is restricted to South Asia, namely Bangladesh, Bhutan, India, and Nepal (Global Tiger Initiative 2010). In the past century, P. tigris numbers have plummeted from 100,000 to below 3,500. Presently, wild P. tigris’ habitat covers approximately 1.2 million km2 in 13 Tiger Range Countries (TRCs) (Global Tiger Initiative 2010). Faced with decreasing P. tigris populations, TRCs in 2010 proposed doubling P. tigris populations by 2022, from a global estimate of ~3,643 in the year 2010 to ~5,845 by the year 2022 under the Global Tiger Recovery Program (Global Tiger Initiative 2010). P. tigris are listed as endangered on the Red List of threatened species by the International Union for Conservation of Nature (IUCN) and under Appendix I by the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES). In Nepal the National Parks and Wildlife Conservation Act, 1973, classified P. tigris as a protected species. India, along with Bhutan, Nepal, Russia and Indonesia, has successfully recovered wild P. tigris populations. In recent years, P. tigris have been recorded at higher elevations outside of their usual habitat (Figure 1). For example, presence of P. tigris was recorded from 3,602 m at Arunachal Pradesh and at 3,274 m in Uttarakhand in India, 4,038 m in Bhutan and 3,165 m from Nepal (Adhikarimayum & Gopi 2018; Bhattacharya & Habib 2016; Tempa et al. 2019). Similarly, the presence of P. tigris was documented at higher elevations in Nepal (i. e., 2,500 m) and in far-western Nepal bordering on Nanda Devi National Park in India, Uttarakhand. A camera trap also recorded P. tigris in Eastern Nepal at 3,165 m (Red Panda Network 2020) bordering on Singalila National Park in India, North Sikkim. P. tigris are not the only species that are being sighted at previously unheard-of altitudes. There have definitely been sightings of several species at higher altitudes. Scientists have also noted an upwards movement of the mountain-dwelling pika (Ochotona roylei and O. macrotis). Within a 46-year interval, the Pika habitat has moved up by 200 m (Koju 2018). Another study, conducted on the clouded leopard (Neofelis nebulosa) in 2020 in the Langtang area, found the elusive animal surviving at 3,498 m (Can et al. 2020). Previously the animal had been found only at 2,300 m. Another study revealed that the house crow (Corvus splendens) has been moving up by 136 m annually on average from 2,000 m to 4,200 m in Mustang district in Nepal (Acharya & Ghimirey 2013). This study concluded that climate change seems to be a possible reason behind this upward movement. And this kind of movement of wildlife has not just been witnessed in the mountains of Nepal. It has also been found with the red panda (Ailurus fulgens), Assam macaque (Macaca assamensis), flying squirrel (Pteromyini), Himalayan crestless porcupine (Hystrix brachyuran), Himalayan goral (Naemorhedus goral), Himalayan palm civet (Paguma larvata), Himalayan serow (Capricornis thar), leopard cat (Prionailurus bengalensis), leopard (Panthera pardus), marbled cat (Pardofelis marmorata), northern red muntjac (Muntiacus vaginalis), yellow-throated marten (Martes flavigula), red fox (Vulpes vulpes), wild boar (Sus scrofa), and the Himalayan black bear (Ursus thibetanus) (Red Panda Network 2020). In Nepal, P. tigris enjoy an exalted status because they are considered sacred and spiritually evolved. Nepalese people generally had a positive attitude toward P. tigris conservation and were willing to accept some losses of livestock, but not human casualties. (Bhattarai & Fischer 2014). Nepal has been a pioneer in P. tigris conservation since it established protected area systems. P. tigris are a priority species for tropical and subtropical ecosystem conservation in Nepal. Until the mid-20th century, P. tigris in Nepal were distributed along the contiguous lowland forests on the slopes of the Siwaliks, Bhabar and alluvial grasslands 44 Management & Pol icy Issues and riverine forests of Nepal (Smythies 1942; Gurung et al. 2006). P. tigris distribution is currently largely limited to five protected areas of the Terai Arc Landscape (TAL), including: Chitwan National Park, Parsa Wildlife Reserve, Bardia National Park, Banke National Park and Shuklaphanta Wildlife Reserve. Conservation activities in Nepal aim to connect several protected areas with habitat corridors to facilitate the movement and dispersal of wildlife primarily along the east-west corridor at lower elevations. TAL in Nepal is critical for doubling the P. tigris population. In Nepal, TAL covers 24,710.13 km2 across 18 districts and extends from the Bagmati River in the east to the Mahakali River along the western border with India. Apart from these protected areas, various national and community forests serve as P. tigris habitats that enable habitat interconnectivity and allow their dispersal. Previously the Bagmati River was considered the eastern boundary of P. tigris distribution in Nepal. In Nepal, P. tigris have been confined largely to the lowland habitat (below 1,000 m elevation) in the forests on the slopes of the Siwalik Range (1,000 to 1,500 m) (Miehe et al. 2016) up to the Bagmati River in the east. However, recent sightings of P. tigris across Nepal at higher elevations raise some critical questions that need to be addressed: a) Did these P. tigris’ seen at higher elevations just stray from their natural habitat? b) Does individual plasticity play a role in the occurrence of these P. tigris’ seen at higher elevations? c) Did a reduction in the prey population, scarcity of water, or elevated temperature force P. tigris to move higher? d) Do these higher elevations historically harbor P. tigris as folklore suggests? The Nepal Himalaya is divided into six biographic and bioclimatic zones in north–south direction: 1) Terai (the northern edge of the Indo-Gangetic plain), 2) Siwalik (Churia) range, 3) Mahabharat range, 4) Midlands, 5) Himalayas, and 6) Inner Himalayas and Tibetan marginal mountains (Figure 2). Each of these zones has distinct altitudinal variation, slope, and relief characteristics, as well as climatic characteristics (Figure 3). The Mahabharat range (also known as mid-hills), south of the Himalayan range and north of the Siwalik range, is a critical physiographic region in Nepal. The Mahabharat range rises higher than the Siwalik hills and reaches an altitude of 3,000 m (Hagen 1998). The Mahabharat is an east-west running mountain range. The Mahabharat has a subtropical climate at low elevations and temperate climates at higher elevations. It is well developed in eastern and central Nepal and underdeveloped in western Nepal. Since the mid-1990s, Nepal’s mid-hills have seen forest cover increase significantly as a result of community forestry. Moreover, mid-hill areas in Nepal have also witnessed a decline in human population due to out-migration and low birth rates. All these factors might have also resulted in P. tigris and other animals coming back in the mid-hills. Present frequent sightings of P. tigris in this range might not be just a fluke. All these sightings might suggest that this range is also an important hotspot for P. tigris and other wildlife populations that need to be protected. Or P. tigris might venture up into Figure 1 – Panthera tigris sightings at high altitudes in Hindu Kush Himalaya.","PeriodicalId":0,"journal":{"name":"","volume":null,"pages":null},"PeriodicalIF":0.0,"publicationDate":"2021-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"1","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"","FirstCategoryId":"93","ListUrlMain":"https://doi.org/10.1553/eco.mont-14-1s43","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 1

Abstract

Nepal’s population of endangered Bengal tigers (Panthera tigris) is on the rise. In recent years, the presence of tigers has been documented at higher elevations. The objective of this study is to explore the possible reasons for the tigers’ presence at the higher elevations. It is critical that these high-altitude habitats for tigers be further explored and protected. The study points out the importance of the Mahabharat range and a longitudinal conservation gradient approach in Nepal. Apart from this, it is imperative to assess the density of tigers and tiger prey in the area. Even though high-altitude ecology may be suitable for tiger growth, the formulation of a high-altitude tiger conservation action plan with effective coordination between stakeholder organizations and concerned departments is of great importance. Tigers are an apex species of the terrestrial ecosystem and exist in a precarious state throughout their range. The tiger is a globally endangered species (Goodrich et al. 2015). In the past, the tiger once existed as nine subspecies, now reduced to only six subspecies that exist in the wild. The subspecies Bengal tiger (Panthera tigris) has the largest population and is restricted to South Asia, namely Bangladesh, Bhutan, India, and Nepal (Global Tiger Initiative 2010). In the past century, P. tigris numbers have plummeted from 100,000 to below 3,500. Presently, wild P. tigris’ habitat covers approximately 1.2 million km2 in 13 Tiger Range Countries (TRCs) (Global Tiger Initiative 2010). Faced with decreasing P. tigris populations, TRCs in 2010 proposed doubling P. tigris populations by 2022, from a global estimate of ~3,643 in the year 2010 to ~5,845 by the year 2022 under the Global Tiger Recovery Program (Global Tiger Initiative 2010). P. tigris are listed as endangered on the Red List of threatened species by the International Union for Conservation of Nature (IUCN) and under Appendix I by the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES). In Nepal the National Parks and Wildlife Conservation Act, 1973, classified P. tigris as a protected species. India, along with Bhutan, Nepal, Russia and Indonesia, has successfully recovered wild P. tigris populations. In recent years, P. tigris have been recorded at higher elevations outside of their usual habitat (Figure 1). For example, presence of P. tigris was recorded from 3,602 m at Arunachal Pradesh and at 3,274 m in Uttarakhand in India, 4,038 m in Bhutan and 3,165 m from Nepal (Adhikarimayum & Gopi 2018; Bhattacharya & Habib 2016; Tempa et al. 2019). Similarly, the presence of P. tigris was documented at higher elevations in Nepal (i. e., 2,500 m) and in far-western Nepal bordering on Nanda Devi National Park in India, Uttarakhand. A camera trap also recorded P. tigris in Eastern Nepal at 3,165 m (Red Panda Network 2020) bordering on Singalila National Park in India, North Sikkim. P. tigris are not the only species that are being sighted at previously unheard-of altitudes. There have definitely been sightings of several species at higher altitudes. Scientists have also noted an upwards movement of the mountain-dwelling pika (Ochotona roylei and O. macrotis). Within a 46-year interval, the Pika habitat has moved up by 200 m (Koju 2018). Another study, conducted on the clouded leopard (Neofelis nebulosa) in 2020 in the Langtang area, found the elusive animal surviving at 3,498 m (Can et al. 2020). Previously the animal had been found only at 2,300 m. Another study revealed that the house crow (Corvus splendens) has been moving up by 136 m annually on average from 2,000 m to 4,200 m in Mustang district in Nepal (Acharya & Ghimirey 2013). This study concluded that climate change seems to be a possible reason behind this upward movement. And this kind of movement of wildlife has not just been witnessed in the mountains of Nepal. It has also been found with the red panda (Ailurus fulgens), Assam macaque (Macaca assamensis), flying squirrel (Pteromyini), Himalayan crestless porcupine (Hystrix brachyuran), Himalayan goral (Naemorhedus goral), Himalayan palm civet (Paguma larvata), Himalayan serow (Capricornis thar), leopard cat (Prionailurus bengalensis), leopard (Panthera pardus), marbled cat (Pardofelis marmorata), northern red muntjac (Muntiacus vaginalis), yellow-throated marten (Martes flavigula), red fox (Vulpes vulpes), wild boar (Sus scrofa), and the Himalayan black bear (Ursus thibetanus) (Red Panda Network 2020). In Nepal, P. tigris enjoy an exalted status because they are considered sacred and spiritually evolved. Nepalese people generally had a positive attitude toward P. tigris conservation and were willing to accept some losses of livestock, but not human casualties. (Bhattarai & Fischer 2014). Nepal has been a pioneer in P. tigris conservation since it established protected area systems. P. tigris are a priority species for tropical and subtropical ecosystem conservation in Nepal. Until the mid-20th century, P. tigris in Nepal were distributed along the contiguous lowland forests on the slopes of the Siwaliks, Bhabar and alluvial grasslands 44 Management & Pol icy Issues and riverine forests of Nepal (Smythies 1942; Gurung et al. 2006). P. tigris distribution is currently largely limited to five protected areas of the Terai Arc Landscape (TAL), including: Chitwan National Park, Parsa Wildlife Reserve, Bardia National Park, Banke National Park and Shuklaphanta Wildlife Reserve. Conservation activities in Nepal aim to connect several protected areas with habitat corridors to facilitate the movement and dispersal of wildlife primarily along the east-west corridor at lower elevations. TAL in Nepal is critical for doubling the P. tigris population. In Nepal, TAL covers 24,710.13 km2 across 18 districts and extends from the Bagmati River in the east to the Mahakali River along the western border with India. Apart from these protected areas, various national and community forests serve as P. tigris habitats that enable habitat interconnectivity and allow their dispersal. Previously the Bagmati River was considered the eastern boundary of P. tigris distribution in Nepal. In Nepal, P. tigris have been confined largely to the lowland habitat (below 1,000 m elevation) in the forests on the slopes of the Siwalik Range (1,000 to 1,500 m) (Miehe et al. 2016) up to the Bagmati River in the east. However, recent sightings of P. tigris across Nepal at higher elevations raise some critical questions that need to be addressed: a) Did these P. tigris’ seen at higher elevations just stray from their natural habitat? b) Does individual plasticity play a role in the occurrence of these P. tigris’ seen at higher elevations? c) Did a reduction in the prey population, scarcity of water, or elevated temperature force P. tigris to move higher? d) Do these higher elevations historically harbor P. tigris as folklore suggests? The Nepal Himalaya is divided into six biographic and bioclimatic zones in north–south direction: 1) Terai (the northern edge of the Indo-Gangetic plain), 2) Siwalik (Churia) range, 3) Mahabharat range, 4) Midlands, 5) Himalayas, and 6) Inner Himalayas and Tibetan marginal mountains (Figure 2). Each of these zones has distinct altitudinal variation, slope, and relief characteristics, as well as climatic characteristics (Figure 3). The Mahabharat range (also known as mid-hills), south of the Himalayan range and north of the Siwalik range, is a critical physiographic region in Nepal. The Mahabharat range rises higher than the Siwalik hills and reaches an altitude of 3,000 m (Hagen 1998). The Mahabharat is an east-west running mountain range. The Mahabharat has a subtropical climate at low elevations and temperate climates at higher elevations. It is well developed in eastern and central Nepal and underdeveloped in western Nepal. Since the mid-1990s, Nepal’s mid-hills have seen forest cover increase significantly as a result of community forestry. Moreover, mid-hill areas in Nepal have also witnessed a decline in human population due to out-migration and low birth rates. All these factors might have also resulted in P. tigris and other animals coming back in the mid-hills. Present frequent sightings of P. tigris in this range might not be just a fluke. All these sightings might suggest that this range is also an important hotspot for P. tigris and other wildlife populations that need to be protected. Or P. tigris might venture up into Figure 1 – Panthera tigris sightings at high altitudes in Hindu Kush Himalaya.
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老虎在其活动范围之外的高海拔地区:这对保护意味着什么?
直到20世纪中期,尼泊尔的底格里斯河沿siwalik、Bhabar和冲冲性草原山坡上的连续低地森林分布。44尼泊尔的管理和政策问题与河流森林(Smythies 1942;Gurung et al. 2006)。底底斯虎的分布目前主要局限于Terai Arc景观(TAL)的五个保护区,包括:Chitwan国家公园、Parsa野生动物保护区、Bardia国家公园、Banke国家公园和Shuklaphanta野生动物保护区。尼泊尔的保护活动旨在将几个保护区与栖息地走廊连接起来,以促进野生动物主要沿着低海拔的东西走廊移动和分散。尼泊尔的TAL对使底格里斯河鼠的数量翻倍至关重要。在尼泊尔,TAL占地24,710.13平方公里,横跨18个地区,从东部的Bagmati河延伸到西部与印度接壤的Mahakali河。除了这些保护区之外,各种国家森林和社区森林是底格里斯河鼠的栖息地,使栖息地相互联系并允许它们扩散。以前,巴格马蒂河被认为是底格里斯河在尼泊尔分布的东部边界。在尼泊尔,底格里斯河主要局限于西瓦里克山脉(1,000至1,500米)斜坡上森林的低地栖息地(海拔低于1,000米)(Miehe et al. 2016),一直到东部的Bagmati河。然而,最近在尼泊尔高海拔地区看到的底格里斯河鼠提出了一些需要解决的关键问题:a)这些在高海拔地区看到的底格里斯河鼠只是偏离了它们的自然栖息地吗?b)个体可塑性是否在高海拔地区的底格里斯河的发生中起作用?c)是猎物数量的减少、水资源的匮乏还是温度的升高迫使底格里斯河鼠向更高的地方迁徙?d)这些较高的海拔是否像民间传说所说的那样,历史上是底格里斯河的港湾?尼泊尔喜马拉雅在南北方向上分为六个生物气候带:1) Terai(印度-恒河平原的北部边缘),2)Siwalik (Churia)山脉,3)Mahabharat山脉,4)Midlands, 5)喜马拉雅山脉,6)内喜马拉雅山脉和西藏边缘山脉(图2)。这些地区都有不同的海拔变化,坡度,地形特征以及气候特征(图3)。Mahabharat山脉(也称为中山)位于喜马拉雅山脉以南和Siwalik山脉以北,是尼泊尔的一个重要地理区域。Mahabharat山脉比Siwalik山还要高,海拔3000米(Hagen 1998)。摩诃婆罗特山脉是一条东西向的山脉。Mahabharat在低海拔地区属于亚热带气候,在高海拔地区属于温带气候。尼泊尔东部和中部发达,西部不发达。自20世纪90年代中期以来,由于社区林业的发展,尼泊尔中部山区的森林覆盖率显著增加。此外,由于外迁和低出生率,尼泊尔中部山区的人口也在减少。所有这些因素也可能导致底格里斯河鼠和其他动物返回中山。目前在这个范围内频繁看到底格里斯河鼠可能不仅仅是侥幸。所有这些发现可能表明,这一范围也是底格里斯河鼠和其他需要保护的野生动物种群的重要热点。或者P. tigris可能会冒险进入图1 -在兴都库什-喜马拉雅山脉高海拔地区发现的Panthera tigris。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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