Hostname: page-component-cd9895bd7-8ctnn Total loading time: 0 Render date: 2024-12-27T11:10:50.900Z Has data issue: false hasContentIssue false

Local community characteristics and potential conflicts around Asian tapir habitat in Batang Gadis National Park, Sumatra, Indonesia

Published online by Cambridge University Press:  23 November 2023

Wanda Kuswanda
Affiliation:
Research Center for Applied Zoology, National Research and Innovation Agency (BRIN), Bogor, West Java, Indonesia
Freddy Jontara Hutapea
Affiliation:
Research Center for Ecology and Ethnobiology, National Research and Innovation Agency (BRIN), Bogor, West Java, Indonesia
Titiek Setyawati
Affiliation:
Research Center for Ecology and Ethnobiology, National Research and Innovation Agency (BRIN), Bogor, West Java, Indonesia
Agus Purwoko*
Affiliation:
Faculty of Forestry, Universitas Sumatera Utara, Padang Bulan Medan, North Sumatra, Indonesia
*
*Corresponding author, [email protected]

Abstract

The Asian tapir Tapirus indicus population has decreased as a result of habitat destruction and degradation, illegal hunting and negative human–tapir interactions. Although this species is categorized as Endangered on the IUCN Red List and is a protected species in Indonesia, where it occurs on Sumatra, studies of its ecology and behaviour and of interactions with people remain limited. We investigated the characteristics of local communities around tapir habitat in Batang Gadis National Park and the interactions of people with tapirs, and assessed the potential for future negative interactions. This study took place in March and October 2021 in Sopotinjak and Pagar Gunung villages. We conducted interviews, using questionnaires, amongst local communities that are familiar with tapirs. The communities belong to the Mandailing Tribe, comprising farmers that frequently access the adjacent forest to support their livelihoods. Local people need protein from animals, but they do not hunt the tapir. Negative human–tapir interactions could potentially increase in the future if tapir browsing intensity in community gardens increases and farmers suffer significant economic losses. We encourage Batang Gadis National Park authorities to develop a human–tapir co-existence management system and to protect tapir habitat.

Type
Short Communication
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
Copyright © The Author(s), 2023. Published by Cambridge University Press on behalf of Fauna & Flora International

The Asian tapir Tapirus indicus is the only Tapirus species inhabiting Southeast Asia (Novarino, Reference Novarino2005; O'Farrill et al., Reference O'Farrill, Galetti and Campos-Arceiz2013). In Indonesia this species occurs only on Sumatra (Holden et al., Reference Holden, Yanuar and Martyr2003). The Asian tapir population continues to decline as a result of habitat loss and fragmentation, human–tapir conflict and localized hunting (Novarino, Reference Novarino2005; Traeholt et al., Reference Traeholt, Novarino, Bin Saaban, Shwe, Lynam and Zainuddin2016; Samantha et al., Reference Samantha, Tee, Kamaruddin, Lechner and Azhar2020). The current estimate of the global Asian tapir population in the wild is < 2,500 individuals (with < 500 individuals on Sumatra), and this is projected to decline a further 20% by 2040 (Traeholt et al., Reference Traeholt, Novarino, Bin Saaban, Shwe, Lynam and Zainuddin2016). The species is categorized as Endangered on the IUCN Red List and is listed in Appendix I of CITES (Traeholt et al., Reference Traeholt, Novarino, Bin Saaban, Shwe, Lynam and Zainuddin2016). In Indonesia the species has been categorized as protected since 1931 (Traeholt et al., Reference Traeholt, Novarino, Bin Saaban, Shwe, Lynam and Zainuddin2016).

Compared to other local wildlife species such as the Sumatran elephant Elephas maximus sumatranus and Sumatran rhinoceros Dicerorhinus sumatrensis, the Asian tapir on Sumatra has received relatively little attention from researchers (Ardiantiono et al., Reference Ardiantiono, Surahmat, Sugiharti, Pusparini, Nurcahyani and Gs2016). Consequently, little is known about the tapir's ecology and behaviour there and of any interactions with people.

Batang Gadis National Park is home to numerous large mammals, including the Asian tapir. This area was designated as a national park in 2004. Located in Mandailing Natal Regency, northern Sumatra, the Park covers c. 1,080 km2 of tropical rainforest at altitudes of 300–2,145 m (Wibisono et al., Reference Wibisono, Figel, Arif, Ario and Lubis2009). It has been reported previously that the Asian tapir density in this National Park is c. 0.09 individuals/ha (Kuswanda & Mukhtar, Reference Kuswanda and Mukhtar2010). The Park is surrounded by local communities, but the impacts of their activities on the tapir population and its ecology are unknown. We studied the characteristics of local communities around tapir habitat in Batang Gadis National Park, the interactions of local people with tapirs, and the potential for negative interactions between people and tapirs and competition between them for resources.

We conducted this study in March and October 2021 in Sopotinjak and Pagar Gunung villages, adjacent to tapir habitat (Fig. 1). The total numbers of households in Sopotinjak and Pagar Gunung are c. 66 and 48, respectively (BPS–Statistics of Mandailing Natal Regency, 2018). We selected 23 and 20 respondents (one respondent per household) in Sopotinjak and Pagar Gunung villages for interviews (Supplementary Material 1). We conducted most of the interviews in Indonesian, and in some cases we hired local interpreters for respondents who could not speak Indonesian. Interviews lasted c. 60–90 min. We also collected information from respondents by asking additional questions that arose during the course of the interviews, and we recorded the responses. We spent 1–2 weeks in each village. Respondents were aged 25–60 years (39 respondents) and > 60 years (4 respondents).

Fig. 1 The location of Sopotinjak and Pagar Gunung villages in Batang Gadis National Park, Sumatra, Indonesia.

The communities of both villages are of the Mandailing Tribe. These communities have lived adjacent to the forest for generations and depend on forest resources for various purposes such as food and medicine. Most villagers were farmers who spent most of their time in their gardens and paddy fields (Table 1). The majority (81.6%) of respondents work in paddy fields. Local people also cultivate a variety of crops, such as vegetables (e.g. pumpkin, corn and cassava), palawija (herbs), durian, cinnamon, jackfruit, bitter beans, river tamarind, coffee and areca nuts. Local people also frequently entered nearby forests to establish new gardens, cut trees, collect firewood, rattan, tree sap (kemenyan Styrax sp. and palm Arenga pinnata), and to hunt for birds and deer. We found that 69.2% of the respondents of Sopotinjak and Pagar Gunung accessed their gardens by crossing or entering tapir habitat in the forests. This situation could potentially increase interactions between people and tapirs as these locations are also where tapirs seek food.

Table 1 The number (and per cent) of local people in Sopotinjak and Pagar Gunung villages in Batang Gadis National Park, Sumatra, Indonesia (Fig. 1) who regularly enter tapir forest habitat, and who engage in various activities in the forest and in their fields.

The Mandailing communities have co-existed with tapirs for years, are aware of the conservation status of the tapir and have positive perceptions of it. We found that 95.7% of respondents in both villages were aware of the existence of tapirs (known as sipan) and believed that tapirs help spread the seeds of plants in Batang Gadis National Park. Local people frequently found plants sprouting from tapir faeces. Tapirs frequently visit the community at night to search for termites, ants and salty soil near habitations. This is in line with previous research reporting that tapirs need salt and minerals to aid digestion (Holden et al., Reference Holden, Yanuar and Martyr2003; Novarino, Reference Novarino2005; Tawa et al., Reference Tawa, Sah and Kohshima2021).

Tapirs frequently cross community gardens and paddy fields to forage. Although local communities often find tapir footprints and faeces in their gardens and rice fields, they rarely encounter tapirs directly because of the species' nocturnal habits (Dutra & Young, Reference Dutra and Young2016). Local people stated that the favourite foods of tapirs are pumpkins, bitter beans, river tamarinds and jackfruits, that they prefer plants that have white gummy latex such as jackfruit leaves, and that tapirs enter community gardens more frequently when people cultivate these crops.

Local people did not react negatively to tapirs browsing in their gardens. There are no records of local communities hunting, killing or poisoning tapirs in this region (Kuswanda et al., Reference Kuswanda, Hutapea, Saputra and Nopandry2023). The fact that the community is dominated by Muslims has prevented local people from hunting and consuming the tapir, which is considered haram (forbidden food) by Muslims because it is regarded as a member of the pig family. Furthermore, nobody hunts tapirs for commercial reasons as there is no local market for their meat.

Tapirs are selective browsers, preferring young leaves, shoots and fruits, and they need a large home range to meet their needs (Maharani et al., Reference Maharani, Harianto, Iswandaru, Winarno, Hasby, Fadillah and Kulsum2019). It is this that results in them entering or crossing community gardens and increases the likelihood they will encounter people. This has been observed in the central Andes of Colombia, where the conversion of forest for potato cultivation has resulted in human–tapir competition, leading to local communities killing and driving out tapirs (Suárez & Lizcano, Reference Suárez and Lizcano2002).

Although we did not record negative interactions between local communities and tapirs around Batang Gadis National Park, competition for vegetation and space will potentially increase in the future if tapir habitat continues to be disrupted and destroyed. The Park authorities need to circumvent any future human–tapir competition by protecting the Park from illegal logging and land encroachment, increasing tapir food plants on tapir trails at Park boundaries and on community lands, providing cultivation training and assistance regarding harvestable plant species that are not preferred by tapirs, and developing an online reporting system through which the community can register concerns regarding tapirs. We also recommend that Batang Gadis National Park develop a human–tapir co-existence management system.

Acknowledgements

We thank BPSILHK Aek Nauli, Batang Gadis National Park, Universitas Sumatra Utara, Bobby Nofriandi, Sri Yanti, Babeh, Erwin, Firman, Mul, Zulfan and other staff for their support during the fieldwork; and the local people of Pagar Gunung and Sopotinjak for sharing their knowledge regarding the Asian tapir.

Author contributions

Study design, fieldwork, data analysis, writing: all authors.

Conflicts of interest

None.

Ethical standards

This study followed the ethical guidelines of the Association of Social Anthropologists of the UK and Commonwealth (Association of Social Anthropologists, 2011), received approval from the Environment and Forestry Research Development Institute of Aek Nauli (Research Permit No ST. 65/BP2LHK ANU-1/Peg.3.0/03/2021) and otherwise abided by the Oryx guidelines on ethical standards.

Footnotes

The supplementary material for this article is available at doi.org/10.1017/S0030605323000789

References

Ardiantiono, , Surahmat, F., Sugiharti, T. & Pusparini, W. (2016) Filling the knowledge gap on the Endangered Asian tapirs in southern part of Tropical Rainforest Heritage of Sumatra. In Proceedings of 3rd International Wildlife Symposium (eds Nurcahyani, E. & Gs, S.), pp. 5057. University of Lampung, Bandar Lampung, Indonesia.Google Scholar
Association of Social Anthropologists (2011) Ethical Guidelines for Good Research Practice. theasa.org/ethics/guidelines.html [accessed 19 August 2022].Google Scholar
BPS–Statistics of Mandailing Natal Regency (2018) Mandailing Natal Regency in Figures: 2018. Badan Pusat Statistik Kabupaten Mandailing Natal, Panyabungan, Indonesia.Google Scholar
Dutra, L.M.L. & Young, R.J. (2016) Can enrichment make Brazilian tapir spend more time on view to the public? Journal of Applied Animal Welfare Science, 18, 7481.CrossRefGoogle Scholar
Holden, J., Yanuar, A. & Martyr, D.J. (2003) The Asian tapir in Kerinci Seblat National Park, Sumatra: evidence collected through photo-trapping. Oryx, 37, 3440.CrossRefGoogle Scholar
Kuswanda, W., Hutapea, F.J., Saputra, M.H. & Nopandry, B. (2023) Species distribution model for the Asian tapir and vegetation characteristics of Batang Gadis National Park, North Sumatra, Indonesia. Tropical Life Science Research, 34, 5780.CrossRefGoogle ScholarPubMed
Kuswanda, W. & Mukhtar, A.S. (2010) Pengelolaan populasi mamalia besar terestrial di Taman Nasional Batang Gadis. Sumatera Utara. Jurnal Penelitian Hutan dan Konservasi Alam, 7, 5974.CrossRefGoogle Scholar
Maharani, N.D., Harianto, S.P., Iswandaru, D. & Winarno, G.D. (2019) Sebaran jenis pakan tapir (Tapirus indicus Desmarest 1819) di Taman Nasional Way kambas (TNWK). In Prosiding Seminar Nasional Biologi 4 (eds Hasby, R.M., Fadillah, A. & Kulsum, Y.), pp. 97104. Pusat Penelitian dan Penerbitan UIN Sunan Gunung Djati, Bandung, Indonesia.Google Scholar
Novarino, W. (2005) Population Monitoring and Study of Daily Activities of Malayan Tapir (Tapirus indicus) Through the Use of the Camera Trapping Technique in Taratak Forest Reserve, Sumatra, Indonesia. Andalas University, Padang, Indonesia.Google Scholar
O'Farrill, G., Galetti, M. & Campos-Arceiz, A. (2013) Frugivory and seed dispersal by tapirs: an insight on their ecological role. Integrative Zoology, 8, 417.CrossRefGoogle ScholarPubMed
Samantha, L.D., Tee, S.L., Kamaruddin, N., Lechner, A.M. & Azhar, B. (2020) Assessing habitat requirements of Asian tapir in forestry landscapes: implications for conservation. Global Ecology and Conservation, 23, e01137.CrossRefGoogle Scholar
Suárez, J.A. & Lizcano, D.J. (2002) Conflict between mountain tapirs (Tapirus bairdii) and farmers in the Colombian central Andes. Tapir Conservation, 11, 1820.Google Scholar
Tawa, Y., Sah, S.A.M. & Kohshima, S. (2021) Salt-lick use by wild Malayan tapirs (Tapirus indicus): behavior and social interactions at salt licks. European Journal of Wildlife Research, 67, 91.CrossRefGoogle Scholar
Traeholt, C., Novarino, W., Bin Saaban, S., Shwe, N.M., Lynam, A., Zainuddin, Z. et al. (2016) Tapirus indicus. In The IUCN Red List of Threatened Species 2016. dx.doi.org/10.2305/IUCN.UK.2016-1.RLTS.T21472A45173636.en.Google Scholar
Wibisono, H.T., Figel, J.J., Arif, S.M., Ario, A. & Lubis, A.H. (2009) Assessing the Sumatran tiger Panthera tigris sumatrae population in Batang Gadis National Park, a new protected area in Indonesia. Oryx, 43, 634638.CrossRefGoogle Scholar
Figure 0

Fig. 1 The location of Sopotinjak and Pagar Gunung villages in Batang Gadis National Park, Sumatra, Indonesia.

Figure 1

Table 1 The number (and per cent) of local people in Sopotinjak and Pagar Gunung villages in Batang Gadis National Park, Sumatra, Indonesia (Fig. 1) who regularly enter tapir forest habitat, and who engage in various activities in the forest and in their fields.

Supplementary material: File

Kuswanda et al. supplementary material

Kuswanda et al. supplementary material
Download Kuswanda et al. supplementary material(File)
File 40.5 KB