Pular para o conteúdo
  • IPÊ
    • Sobre o IPÊ
    • Missão
    • Nosso Credo
    • Governança
    • Staff Senior
    • Ipeanos
    • Estratégias
    • Apoiadores e Parceiros
    • Prêmios
    • Imprensa
    • Onde Estamos
    • Nossos Resultados
    • Relatórios Anuais
    • Seja nosso Parceiro
  • Doe Agora
    • Doe Florestas
    • Por que doar?
    • Arredonde Suas Compras
    • Doe com PayPal ou Conta Corrente
    • Doações internacionais
    • Adote uma Espécie
    • Proteja o Sistema Cantareira
  • Notícias
    • Últimas Notícias
  • Projetos
    • Baixo Rio Negro
    • Nazaré Paulista
    • Pantanal e Cerrado
    • Sul da Bahia
    • Pontal do Paranapanema
    • Projetos Temáticos
      • Voluntariado para Conservação
      • Pesquisa e Desenvolvimento / P&D
      • Áreas Protegidas
      • Integração Escola e Comunidade
      • Projeto Escolas Climáticas
      • Paisagens climáticas
      • Centro de Educação e Cooperação Socioambiental para o Clima
  • Negócios Sustentáveis
    • Marketing Relacionado a Causas
    • Cases de MRC
    • Modelos de Parcerias
    • Iniciativas para Doação
  • Soluções em Educação
    • Escas
    • Mestrado Profissional
    • Pós-graduação
    • Cursos de Curta Duração
  • Publicações
    • Flora Regional
    • Boas Práticas em UCs
    • Atlas Cantareira
    • Artigos Científicos
    • Séries Técnicas, Guias e Outros Materiais
  • Estatuto
  • Código de Ética
  • Parcerias Públicas
  • Fale Conosco
  • Português

Large wild herbivores reduce the fast biodiversity decline of plants in a tropical forestry hotspot

9 de novembro de 2021 Por Paula Piccin

::cck::896::/cck::
::introtext::

For 10 years, in the Atlantic Forests, researchers compared forests used by herbivorous mammals, including the lowland tapir (Tapirus terrestris) and the white-lipped peccary (Tayassu pecari), and areas in which these animals have been barred from access due to exclosure plots (fences). The main conclusion is that the areas used by these herbivores show lower loss of diversity than fenced areas.

The new study on tropical forests has generated an article recently published in the Journal of Applied Ecology of the British Ecological Society (BES). The research was performed at Morro do Diabo State Park, in the far west of the state of São Paulo. The work warns of the importance of conservation of animals that are facing extinction. The lowland tapir, for example, is classified as Vulnerable in the IUCN (International Union for Conservation of Nature) Red List throughout its distribution range. The white-lipped peccary, in turn, is listed as Critically Endangered in the Atlantic Forest.

Patrícia Medici, coordinator of the Lowland Tapir Conservation Initiative (LTCI) at IPÊ (Institute for Ecological Research), authors the article alongside Nacho Villar, a researcher of the NIOO-KNAW Dutch Institute for Ecology. “In this study, we recorded the results of a first experiment on the effects of conservation and protection of large herbivores on the maintenance of biodiversity in tropical forests and, to the extent we know, in any other forest biome. The study shows that large herbivores play an important role in the deceleration of the loss of forest diversity”, says Medici.

According to the study, mature forests with great diversity were those that benefited the most from the presence of large herbivores. “The results show how forest composition is severely affected when the animals are excluded from the biome, a sign of what may be happening in a series of other fragments of the Atlantic Forest, one of the most endangered biomes on the planet,” points out the researcher.

With the launching of the Decade on Restoration of the United Nations (2021 -2030), the results of this study also serve as guidance for future initiatives on forest conservation and restoration. “Conservation of these animals and trophic rewilding (without human participation) are gaining momentum as important tools to restore forest ecosystems and avoid the acute effects of global changes on biodiversity. However, such nature-based solutions are not yet recognized as a conservation option, especially in tropical forests. We believe that this study strengthens the strategic aspect of following in this direction,” points out the researcher.

Such findings demonstrate that species conservation and the restoration they promote may be more efficient in protecting against strong declines of diversity in the long run, particularly in well preserved tropical forests with high levels of forest diversity. “Throughout the 10 years of the study, the abundance of plants in the initial stage of germination, their recruitment and species richness fell by some 20% or more, providing a unique natural experiment to test the functional significance of large herbivores to avoid the collapse of biodiversity in the long run,” says Medici.

Researchers also observed whether large herbivores have a different effect on mature and secondary forests. “This is an important question and has not yet been explored in trophic rewilding. In secondary forests, we identified ca. half the number of species when compared with mature forests. In secondary forests, the results show limited protection by large herbivores against the loss of diversity. Long-run regional environmental changes place the restoration of such secondary forests at risk, and their transition to more mature and diversified forests,” says Nacho Villar.

Details of the research in practice

The discoveries are the result of monitoring 200 m2 of Atlantic Forest in Morro do Diabo State Park, São Paulo, Brazil, between 2004 and 2014. “We studied the potential role of large herbivores against the collapse of plant diversity through time, examining their effect on the abundance of plants in the initial phase of germination, as well as species richness and diversity, the temporal diversity and the rate of change of forest composition. These animals contribute directly to the plants in the forest understory, through seed dispersal and how they affect plants in the early phase of germination. Thus, biodiversity strongholds are highly sensitive to the disappearance of animals like the lowland tapir (Tapirus terrestris) and the white-lipped peccary (Tayassu pecari), for example,” explains Villar.

Medici’s team established 200 plots in the monitored area, including 100 fenced plots to prevent the access of large herbivores, and 100 control plots, where there was no restriction to the entry of the animals. In order to understand the possible differences in the maturity of the forest, the fenced areas were divided into two large groups, being 25 pairs in areas of mature forest, and 25 pairs in secondary forest.

For insulation of the areas (exclosure plots), the researchers used wooden posts and poultry netting (2×2 cm). The exclusion areas had the following dimensions: 3 meters in width, 6 meters in length, and 1.20 meter in height. A 20 cm opening was maintained along the bottom of the plot, allowing for the entry of small terrestrial mammals, such as rodents and marsupials. Within the exclosure plots, a central sampling area of 1×4 m was established, and it was divided into four 1×1 m quadrants.

Control plots that were not fenced were 1 m wide and 4 m long, divided into 4 quadrants of 1×1 m. For each exclosure and control plot, each of the 1×1 m quadrants was chosen randomly for sampling throughout the study.

Forest sampling

In the monitored quadrants, all plants with a diameter of over 10 cm and diameter ≤ 5 cm were marked with PVC tags and received reference numbers. This methodology permitted the subsequent sampling of the same individuals. New plants that germinated during the study and complied with the criteria were incorporated into the monitoring protocol.

Throughout the first five years of the study (2004-2008), the researchers measured the plants twice a year, in the early rainy season (October) and in early dry season (April). From 2009 to 2012, data collection took place once a year. The final measurements took place in 2014, ending 10 years of data collection, with a total of 14 measurements. “We followed the fate of 7,287 plants and traced the decline of diversity over 10 years,” points out Medici.

Threats and opportunity

The conservation of large herbivores and the restoration of forests affected by them, especially tropical forests, is a challenge due to a series of threats that these animals face. According to the researchers, advances in this direction must consider measures for species protection. “Effective management of the landscape, protection and conservation aimed at increasing the populations of these animals and the facilitation of dispersal and movement between remaining forest areas are strategic. Furthermore, it is worth pointing out the need for reintroduction and translocation initiatives, given that large extensions of mature forest, rich in diversity, are currently being deprived of these animals due to hunting, roadkill and so many other threats.” 

Based on the results, the researchers point out that the active restoration of neotropical forests with large herbivores may, in fact, be the most efficient solution to improve the state of conservation of many species of large herbivores, contributing to the diversity of tropical forests in the long run. “We suggest that the measures begin in mature forests and then proceed to secondary forests with high levels of diversity.”

::/introtext::
::fulltext::::/fulltext::
::cck::896::/cck::

Categorias News
Quatro assentamentos participam de projeto no ES
Artigo: Ansiedade climática ou ecoansiedade e a educação ambiental

Deixe um comentário Cancelar resposta

Posts Recentes

  • REFLORA realiza oficina para fortalecer negócios sustentáveis da Amazônia 
  • ESCAS-IPÊ assina cooperação com Fundação Matias Machline para Mestrado
  • Governo federal assina decreto que estabelece a nova Estratégia e Plano de Ação Nacionais para a Biodiversidade (EPANB)
  • IPÊ, Esalq-USP e Imperial College lançam recomendações para a implementação do PLANAVEG 2025-2028 junto a proprietários rurais 
  • Campeonato de futebol em Reserva da Amazônia ajuda na restauração do bioma com apoio do projeto REFLORA

Publicações

  • junho 2025
  • maio 2025
  • abril 2025
  • março 2025
  • fevereiro 2025
  • janeiro 2025
  • dezembro 2024
  • novembro 2024
  • outubro 2024
  • setembro 2024
  • agosto 2024
  • julho 2024
  • junho 2024
  • maio 2024
  • abril 2024
  • março 2024
  • fevereiro 2024
  • janeiro 2024
  • dezembro 2023
  • novembro 2023
  • outubro 2023
  • setembro 2023
  • agosto 2023
  • julho 2023
  • junho 2023
  • maio 2023
  • abril 2023
  • março 2023
  • fevereiro 2023
  • janeiro 2023
  • dezembro 2022
  • novembro 2022
  • outubro 2022
  • setembro 2022
  • agosto 2022
  • julho 2022
  • junho 2022
  • maio 2022
  • abril 2022
  • março 2022
  • fevereiro 2022
  • janeiro 2022
  • dezembro 2021
  • novembro 2021
  • outubro 2021
  • setembro 2021
  • agosto 2021
  • julho 2021
  • junho 2021
  • maio 2021
  • abril 2021
  • março 2021
  • fevereiro 2021
  • janeiro 2021
  • dezembro 2020
  • novembro 2020
  • outubro 2020
  • setembro 2020
  • agosto 2020
  • julho 2020
  • junho 2020
  • maio 2020
  • abril 2020
  • março 2020
  • fevereiro 2020
  • janeiro 2020
  • dezembro 2019
  • novembro 2019
  • outubro 2019
  • setembro 2019
  • agosto 2019
  • julho 2019
  • junho 2019
  • maio 2019
  • abril 2019
  • março 2019
  • fevereiro 2019
  • janeiro 2019
  • dezembro 2018
  • novembro 2018
  • outubro 2018
  • setembro 2018
  • agosto 2018
  • julho 2018
  • junho 2018
  • maio 2018
  • abril 2018
  • março 2018
  • fevereiro 2018
  • janeiro 2018
  • dezembro 2017
  • novembro 2017
  • outubro 2017
  • setembro 2017
  • agosto 2017
  • julho 2017
  • junho 2017
  • maio 2017
  • abril 2017
  • março 2017
  • fevereiro 2017
  • janeiro 2017
  • dezembro 2016
  • novembro 2016
  • outubro 2016
  • setembro 2016
  • agosto 2016
  • julho 2016
  • junho 2016
  • maio 2016
  • janeiro 2016
  • dezembro 2015
  • novembro 2015
  • outubro 2015
  • setembro 2015
  • agosto 2015
  • julho 2015
  • junho 2015
  • maio 2015
  • abril 2015
  • março 2015
  • fevereiro 2015
  • janeiro 2015
  • dezembro 2014
  • novembro 2014
  • outubro 2014
  • setembro 2014
  • agosto 2014
  • julho 2014
  • junho 2014
  • maio 2014
  • abril 2014
  • março 2014
  • fevereiro 2014
  • janeiro 2014
  • dezembro 2013
  • novembro 2013
  • outubro 2013
  • setembro 2013
  • julho 2013
  • junho 2013
  • maio 2013

Categorias

  • Áreas Protegidas
  • Baixo Rio Negro
  • Boas Práticas
  • Cases de MRC
  • Centro de Educação e Cooperação Socioambiental para o Clima
  • COP-16 Agenda
  • COP16
  • Cursos
  • Depoimentos
  • Doe
  • Home
  • Iniciativas para Doação
  • IPÊ
  • IPÊ
  • Não categorizado
  • Negócios Sustentáveis
  • Notícias
  • Paisagens Climáticas
  • Pesquisa e Desenvolvimento
  • Pontal do Paranapanema
  • Projetos
  • Projetos Temáticos
  • publicacoes
  • ra.2022
  • Relatórios Anuais
  • Uncategorised

Onde Estamos

Rod. Dom Pedro I, km 47
Nazaré Paulista, SP, Brasil
Caixa Postal 47 – 12960-000
Tel: (11) 3590-0041

Mapa para o IPÊ
Escritórios

Redes Sociais

  • Facebook
  • Twitter
  • Instagram
  • Youtube
  • Linkedin

Política de Privacidade
Ouvidoria

Termos de Uso | Estatuto
Copyright © Ipê – Instituto de Pesquisas Ecológicas.
Email: ipe@ipe.org.br

plugins premium WordPress
  • Português