Lowland Tapir (Tapirus terrestris)
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IUCN · Vulnerable

Lowland Tapir

Tapirus terrestris

Photo: Charles J. Sharp / CC BY-SA 4.0

The lowland tapir is the largest native land mammal in South America and one of the continent's most ecologically influential herbivores. As the last surviving megafrugivore across much of its range, it swallows large fruits whole and carries their seeds far from the parent tree, earning it a reputation as a "gardener of the forest" whose foraging shapes the composition of tropical woodlands [Tobler et al. 2010; O'Farrill et al. 2013]. Yet the species has declined by an estimated 30% over the past three generations and is now classified as Vulnerable on the IUCN Red List [Varela et al. 2019]. This profile examines the tapir's biology, its keystone role in seed dispersal and carbon storage, the pressures driving its decline, and the long-term programs working to keep it on the landscape.


Biology and Identification

The lowland tapir is a stocky, barrel-bodied ungulate with a short, prehensile proboscis formed from the upper lip and nose. Adults typically weigh between 150 and 250 kg, with a head-body length of roughly 180–220 cm and a shoulder height of about 77–108 cm; females tend to be slightly larger than males [Padilla & Dowler 1994]. The coat is dark brown to grey-black, and a distinctive erect mane runs along the neck. Newborn calves are reddish-brown and patterned with white spots and stripes — camouflage that fades within the first several months of life [Padilla & Dowler 1994].

As an odd-toed ungulate (order Perissodactyla), the tapir is more closely related to horses and rhinoceroses than to deer or pigs. It is a hindgut-fermenting herbivore that browses leaves, shoots, aquatic vegetation, and a large quantity of fruit. Tapirs are strong swimmers and divers, frequently taking refuge in rivers and wetlands, and they are largely nocturnal and crepuscular [Padilla & Dowler 1994]. Reproduction is slow: females produce a single calf after a gestation of roughly 13–14 months, a low reproductive rate that makes populations slow to recover from losses [Padilla & Dowler 1994].

The tapir's ecological signature lies in its diet. In the Peruvian Amazon, analysis of dung samples documented the seeds of 122 plant species passing through tapirs, the great majority deposited intact and viable [Tobler et al. 2010]. Because tapirs ingest and move large seeds that few other surviving animals can handle, they provide a non-redundant dispersal service for many large-seeded, high-wood-density trees [Bello et al. 2015].


Habitat and Range

The lowland tapir occupies the widest distribution of any living tapir, ranging from north-central Colombia and east of the Andes through Venezuela, the Guianas, Ecuador, Peru, Bolivia, Brazil, Paraguay, and into northern Argentina [Varela et al. 2019]. It reaches its greatest abundance in the lowland rainforests of the Amazon Basin but also persists in seasonally dry and open habitats, including the Cerrado savanna, the Pantanal wetlands, and the Gran Chaco of Bolivia and Paraguay [Varela et al. 2019].

The species' range has contracted most severely in the Atlantic Forest of eastern South America, where deforestation has reduced suitable habitat to a small fraction of its original extent. A comprehensive assessment estimated that 2,665–15,992 tapirs remain in 48 confirmed populations occupying roughly 26,654 km² — about 1.78% of the biome's original area — and that only a handful of those populations are likely to remain viable over the next century without intervention [Flesher & Medici 2022].

In accordance with NRWL sensitive-species policy, specific site locations, corridor routes, and seasonal movement details are not disclosed in this article.


Conservation Status

The lowland tapir is listed as Vulnerable on the IUCN Red List under criteria A2cde+3cde, assessed in 2019 [Varela et al. 2019]. The classification reflects an estimated population reduction of slightly more than 30% over the past three generations (about 33 years), driven by habitat loss, illegal hunting, road mortality, and competition with livestock, with the population trend listed as decreasing [Varela et al. 2019]. The species is also included on CITES Appendix II, which regulates international commercial trade in the species and its parts [CITES 2023].

Range-wide population figures are uncertain because tapirs occur at naturally low densities and are difficult to survey, but regional assessments make the trajectory clear. In the Atlantic Forest, where the species is most imperiled, fewer than an estimated 16,000 individuals persist in fragmented and largely isolated subpopulations, many of which fall below thresholds for long-term demographic and genetic viability [Flesher & Medici 2022]. Across the Amazon and other strongholds the species remains more widespread, but local declines are documented wherever hunting pressure and habitat conversion intensify [Varela et al. 2019].


Threats

Habitat loss and fragmentation are the dominant long-term threats. Conversion of forest and savanna to cattle pasture, soy and oil-palm cultivation, mining, and infrastructure has reduced and divided tapir habitat across the range, isolating populations and eroding their genetic connectivity [Flesher & Medici 2022].

Hunting for meat remains a serious pressure, particularly along expanding road networks, settlement frontiers, and the agricultural margins of the Amazon Basin. Because tapirs reproduce slowly, even modest levels of offtake can drive local populations toward extinction [Varela et al. 2019].

Road mortality is a substantial and growing threat in fragmented landscapes. Studies in the Brazilian Cerrado document tapirs killed in vehicle collisions, with post-mortem examinations attributing death to skeletal fractures and severe internal trauma; on some monitored highways dozens of tapirs are killed over a few years [Navas-Suárez et al. 2019].

Agrochemical exposure compounds these pressures. The first toxicological survey of wild lowland tapirs detected carbamate and organophosphate pesticides, pyrethroids, and toxic metals including cadmium and lead in tapir tissues — some at concentrations capable of causing adverse health effects — and found macroscopic liver or kidney alterations in 90% of road-killed tapirs examined [Medici et al. 2021].

Competition with livestock and disease transmission from domestic animals add further strain where cattle ranching overlaps tapir habitat [Varela et al. 2019].


What Is Being Done

Long-term field research. The Lowland Tapir Conservation Initiative (LTCI), founded by Patrícia Medici and run by Brazil's Institute for Ecological Research (IPÊ / Instituto de Pesquisas Ecológicas), has studied tapirs continuously since 1996 across the Atlantic Forest, Pantanal, Cerrado, and Amazon. The program combines camera-trapping, GPS-telemetry, and veterinary health assessment to track population trends and inform conservation policy [Medici et al. 2022].

Road-ecology mitigation. Building on documented roadkill hotspots, LTCI and partners in Mato Grosso do Sul have worked to reduce tapir vehicle deaths through measures such as speed-monitoring cameras, road signage, and driver-awareness campaigns, while research continues to map where wildlife crossings are most needed [Navas-Suárez et al. 2019; Medici et al. 2022].

Movement and connectivity science. GPS-tracking research has quantified how tapirs adjust their movement across gradients of human disturbance, providing the spatial data needed to design and protect functional corridors between fragmented populations [Medici et al. 2022].

Demonstrating ecological value. Peer-reviewed work documenting the tapir's role in dispersing seeds — including in burned and degraded Amazonian forest, where tapirs deposit large numbers of seeds and can aid recovery — strengthens the scientific case for conservation by linking tapirs to forest regeneration and carbon storage [Paolucci et al. 2019; Bueno et al. 2013; Bello et al. 2015].

Capacity building and education. LTCI invests in training local researchers and in environmental-education programs with schools and communities in tapir range areas, aiming to reduce hunting pressure and build durable local support for the species [Medici et al. 2022].


How Readers Can Help

Citizen science. Log wildlife observations on platforms such as iNaturalist. Verified occurrence records help refine range maps and feed into IUCN assessments and connectivity planning.

Policy engagement. Support policies that protect tropical forests and savannas, strengthen enforcement against illegal hunting and trade, and incorporate wildlife crossings into road and infrastructure planning. Upholding CITES Appendix II commitments helps regulate international trade in the species [CITES 2023].

Informed consumer choices. Favor products and supply chains that do not drive deforestation in the Amazon, Cerrado, Atlantic Forest, and Pantanal, where agricultural expansion is the principal driver of tapir habitat loss [Flesher & Medici 2022].

Support credible field programs. Long-term research and conservation organizations such as IPÊ's Lowland Tapir Conservation Initiative depend on sustained funding to maintain monitoring, road-mitigation, and education work across multiple biomes [Medici et al. 2022].

Education outreach. Share accurate, science-based information about the tapir's role as a seed disperser and forest gardener. Public appreciation of that ecological function builds support for protecting the species and the forests it sustains [O'Farrill et al. 2013].


References

[Bello et al. 2015]     Bello, C., Galetti, M., Pizo, M.A., Magnago, L.F.S., Rocha, M.F., Lima, R.A.F., Peres, C.A.,     Ovaskainen, O. & Jordano, P. (2015). Defaunation affects carbon storage in tropical forests.     Science Advances, 1(11), e1501105. https://doi.org/10.1126/sciadv.1501105

[Bueno et al. 2013]     Bueno, R.S., Guevara, R., Ribeiro, M.C., Culot, L., Bufalo, F.S. & Galetti, M. (2013). Functional     redundancy and complementarities of seed dispersal by the last Neotropical megafrugivores.     PLOS ONE, 8(2), e56252. https://doi.org/10.1371/journal.pone.0056252

[CITES 2023]     CITES. (2023). Appendices I, II and III. Convention on International Trade in Endangered Species     of Wild Fauna and Flora. https://cites.org/eng/app/appendices.php

[Flesher & Medici 2022]     Flesher, K.M. & Medici, E.P. (2022). The distribution and conservation status of Tapirus     terrestris in the South American Atlantic Forest. Neotropical Biology and Conservation,     17(1), 1–19. https://doi.org/10.3897/neotropical.17.e71867

[Medici et al. 2021]     Medici, E.P., Fernandes-Santos, R.C., Testa-José, C., Godinho, A.F. & Brand, A.F. (2021).     Lowland tapir exposure to pesticides and metals in the Brazilian Cerrado. Wildlife Research,     48(5), 393–403. https://doi.org/10.1071/WR19183

[Medici et al. 2022]     Medici, E.P., Mezzini, S., Fleming, C.H., Calabrese, J.M. & Noonan, M.J. (2022). Movement     ecology of vulnerable lowland tapirs between areas of varying human disturbance.     Movement Ecology, 10, 14. https://doi.org/10.1186/s40462-022-00313-w

[Navas-Suárez et al. 2019]     Navas-Suárez, P.E., Díaz-Delgado, J., Fernandes-Santos, R.C., Testa-José, C., Silva, R.,     Sansone, M., Medici, E.P. & Catão-Dias, J.L. (2019). Pathological findings in lowland tapirs     (Tapirus terrestris) killed by motor vehicle collision in the Brazilian Cerrado.     Journal of Comparative Pathology, 170, 34–45. https://doi.org/10.1016/j.jcpa.2019.05.004

[O'Farrill et al. 2013]     O'Farrill, G., Galetti, M. & Campos-Arceiz, A. (2013). Frugivory and seed dispersal by tapirs:     an insight on their ecological role. Integrative Zoology, 8(1), 4–17.     https://doi.org/10.1111/j.1749-4877.2012.00316.x

[Padilla & Dowler 1994]     Padilla, M. & Dowler, R.C. (1994). Tapirus terrestris. Mammalian Species, 481, 1–8.     https://doi.org/10.2307/3504109

[Paolucci et al. 2019]     Paolucci, L.N., Pereira, R.L., Rattis, L., Silvério, D.V., Marques, N.C.S., Macedo, M.N. &     Brando, P.M. (2019). Lowland tapirs facilitate seed dispersal in degraded Amazonian forests.     Biotropica, 51(2), 245–252. https://doi.org/10.1111/btp.12627

[Tobler et al. 2010]     Tobler, M.W., Janovec, J.P. & Cornejo, F. (2010). Frugivory and seed dispersal by the lowland     tapir Tapirus terrestris in the Peruvian Amazon. Biotropica, 42(2), 215–222.     https://doi.org/10.1111/j.1744-7429.2009.00549.x

[Varela et al. 2019]     Varela, D., Flesher, K., Cartes, J.L., de Bustos, S., Chalukian, S., Ayala, G. & Richard-Hansen, C.     (2019). Tapirus terrestris. The IUCN Red List of Threatened Species 2019: e.T21474A45174127.     https://dx.doi.org/10.2305/IUCN.UK.2019-1.RLTS.T21474A45174127.en

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