The yellow-headed tortoise Indotestudo elongata is widely distributed throughout South and Southeast Asia, ranging across northern India, Nepal, Bhutan, Bangladesh, Thailand, Viet Nam, Cambodia, Laos and Malaysia (Rahman et al., Reference Rahman, Platt, Das, Choudhury, Ahmed and Cota2019). It lives at low to mid elevations, primarily in evergreen and deciduous forests, grasslands and secondary forests (Schleich & Kästle, Reference Schleich and Kästle2002; Ihlow et al., Reference Ihlow, Dawson, Hartmann, Som, Rhodin, Pritchard, van Dijk, Saumure, Buhlmann, Iverson and Mittermeier2016). In Nepal its distribution has been recorded in the lowland Terai from Jhapa District in the far east to Shuklaphanta National Park in the far west (Aryal et al., Reference Aryal, Dhamala, Bhurtel, Suwal and Rijal2010; Rawat et al., Reference Rawat, Bhattarai, Poudyal and Subedi2020). Human-induced forest fires, habitat loss, excessive collection for food, traditional medicinal uses and as pets in temples and houses, and targeted hunting with dogs, for trade, are the major threats facing the species (Kästle et al., Reference Kästle, Rai and Schleich2013; Ihlow et al., Reference Ihlow, Dawson, Hartmann, Som, Rhodin, Pritchard, van Dijk, Saumure, Buhlmann, Iverson and Mittermeier2016). It is categorized as Critically Endangered on the IUCN Red List (Rahman et al., Reference Rahman, Platt, Das, Choudhury, Ahmed and Cota2019), and is also listed in Appendix II of CITES (Ihlow et al., Reference Ihlow, Dawson, Hartmann, Som, Rhodin, Pritchard, van Dijk, Saumure, Buhlmann, Iverson and Mittermeier2016).
Jalthal Forest in the eastern lowland of Nepal is a remnant of a once continuous, dense and lush forest called Charkoshe Jhadi (Fig. 1). It spans 62.6 km2 and comprises floristic elements from the Indo-Malayan Floristic Region, consisting of dominant sal Shorea robusta forest and mixed deciduous forest (Thapa et al., Reference Thapa, Bhatta and Khatri2003). The climate is mostly tropical monsoon with a dry and warm summer (March–mid May), a humid and warm period (mid May–October) and a dry and cold winter (November–February; Bhattarai, Reference Bhattarai2017). Mean annual minimum and maximum temperatures are 10 and 33 °C, respectively. The forest is home to a high diversity of plant and animal species, including threatened vertebrates such as the Chinese pangolin Manis pentadactyla, Asian elephant Elephas maximus and leopard Panthera pardus. Isolated populations, invasive plant species (e.g. Mikania micrantha and Chromolaena odorata), wildlife hunting, biomass collection, road development in the forest and forest fires are the direct threats to Jalthal Forest (Sharma et al., Reference Sharma, Tamang, Poudel, Subba, Timsina and Adhikari2021).
Jalthal Forest is one of the last remnants of suitable habitat for the Critically Endangered I. elongata in eastern lowland Nepal but there is limited information on the distribution of and threats facing this species there. During 25–31 August 2021, we conducted 55 structed interviews with members of community forest user groups to identify the probable locations and habitats of I. elongata. From the interviews we identified 45 potential locations, and we then conducted surveys within an area of c. 0.25 km2 at each location. We conducted three field surveys during September–November 2021, on foot. We conducted the initial survey on 3–16 September, followed by surveys on 5–12 October and 4–11 November. We surveyed 22 community forests for a total of 240 h. Because of the elusive nature of I. elongata, we surveyed open and dense vegetation, fallen leaves and tree trunks and porcupine and pangolin burrows (van Dijk, Reference van Dijk1998), and searched for indirect signs of footprints and triangular bite marks on vegetation characteristic of the species (Sriprateep et al., Reference Sriprateep, Aranyavalai, Aowphol and Thirakhupt2013; Deepak & Vasudevan, Reference Deepak and Vasudevan2015). In total we surveyed 25.4% (11.25 km2) of Jalthal Forest and recorded only four mature individuals of I. elongata, giving a naïve population density of 0.35/km. We did not observe any indirect signs of the species.
From 25 August to 11 November 2021 we also interviewed 80 people (including 10 local hunters) who were dependent on the forest for their livelihood. Each interview lasted c. 20 min and included open-ended questions about socio-demographic characteristics, background, motivation, local knowledge and trends and perceptions regarding the species (Supplementary Material 1). We found that 90% of the respondents knew I. elongata inhabited Jalthal Forest, and 33% of the respondents admitted they had killed I. elongata in their lifetime; 42% believed the species is decreasing because of hunting and/or incursion of invasive species (30%), and the remaining 28% were unsure of the cause of this decrease. Nine of the hunters were from the eastern (n = 6) and southern (n = 3) parts of the forest, were aged 35–55 and belonged to the Meche and Sathar communities. These are Indigenous local tribes that hunt traditionally. Based on the interviews we determined that 34 I. elongata individuals had been hunted during 2017–2021, an annual mean of 6.8, and that the numbers hunted were decreasing. The purpose of hunting was for consumption (70% of respondents) and ethnomedicinal purposes (30% of respondents).
During June–August 2022, through information gained from local people, one I. elongata was handed to the Turtle Rescue and Conservation Center, Nepal, through coordination with Forest Action Nepal (Plate 1), two individuals were successfully released by the community forest user groups in Jalthal Forest, but two other individuals (Plate 2) were killed.
Information from the interviews, and our surveys, suggest this isolated population of I. elongata is small and severely threatened. Compared to north-east Thailand, where a density of 243 per km2 has been recorded (Sriprateep et al., Reference Sriprateep, Aranyavalai, Aowphol and Thirakhupt2013), the density of I. elongata in Jalthal Forest is low. That we recorded only a few I. elongata could, however, be in part a result of surveying during the drier, cooler time of year, when I. elongata is less active (van Dijk, Reference van Dijk1998), and the disturbance at this time of year from people entering the forest to collect edible mushrooms and ferns (authors, pers. obs.). On the other hand, of the 45 potential survey locations, 25 had a dense ground cover (mean 74 ± SD 12%) comprised principally of the invasive alien M. micrantha. An area of 29.4 km2 of Jalthal Forest has been invaded by alien plant species, of which 8.8 km2 has been heavily invaded (Tamang & Sharma, Reference Tamang, Sharma, Roshetko and Meybeck2021). A dense cover of M. micrantha could negatively affect the foraging and basking of I. elongata.
The distribution range of a species influences its risk of extinction, as smaller-ranging species have lower genetic variation and lower genetic plasticity compared to wider-ranging congeners (Brown, Reference Brown1984; Gaston, Reference Gaston2003; Meiri et al., Reference Meiri, Bauer, Allison, Chirio, Colli and Das2017; Novosolov et al., Reference Novosolov, Rodda, North, Butchart, Tallowin, Gainsbury and Meiri2017). In this context, climate change, introduced species, pathogens, cataclysms and habitat change can drive isolated, small-ranging species to extinction (Caughley, Reference Caughley2013; Meiri et al., Reference Meiri, Bauer, Allison, Chirio, Colli and Das2017). These threats already exist in Jalthal Forest and, combined with a slow reproductive cycle (males and females reach sexual maturity at 6 and 8 years, respectively; Sriprateep et al., Reference Sriprateep, Aranyavalai, Aowphol and Thirakhupt2013), local hunter-gatherer practices could drive the small population of I. elongata in Jalthal Forest to extinction.
Considering the threats to I. elongata we recommend strong conservation interventions by local government and conservation organizations. Additionally, awareness campaigns focused on local hunters, promoting allopathic medicine rather than the use of animal body parts, further research to assess the impacts of invasive species on I. elongata, and establishment of communication networks amongst community forest user groups and other stakeholders are required to conserve this species in Jalthal Forest.
Author contributions
Study design: both authors; fieldwork, data analysis, writing: AS; revision: both authors.
Acknowledgements
We acknowledge financial support from Forest Action Nepal via a Darwin Initiative project (REF 26-022) and we thank all members of the community forest user groups. We thank the Nepal Ministry of Forests and Environment for permission to conduct the study
Conflicts of interest
None.
Ethical standards
Interviews were conducted in accordance with the standards of the Association of Social Anthropologists of the UK and Commonwealth, and this research otherwise abided by the Oryx guidelines on ethical standards. The study did not involve specimen collection or animal experimentation.
Data availability
The data that support the findings of this study are available from the corresponding author upon reasonable request.