Temporal evolution of deforestation in the Xingu River Watershed between 2008 to 2020

Authors

  • Antonio Henrique Cordeiro Ramalho henriqueramalho14@gmail.com
    1Universidade Federal do Oeste do Pará - UFOPA, Instituto de Biodiversidade e Floresta, Santarém, PA
  • Fernanda Dalfiôr Maffioletti fernandamaffioletti040@gmail.com
    Universidade Federal do Espírito Santo – Departamento de Ciências Florestais e da Madeira, Centro de Ciências Agrárias e Engenharias
  • Leonardo Duarte Biazatti leo-biazatti@live.com
    2Universidade Federal do Espírito Santo – Departamento de Ciências Florestais e da Madeira, Centro de Ciências Agrárias e Engenharias
  • Gabriel Severo Carvalho gabriel.carvalho.67@edu.ufes.br
    Universidade Federal do Espírito Santo – Departamento de Ciências Florestais e da Madeira, Centro de Ciências Agrárias e Engenharias
  • Marcos Antoni Antoni Pinheiro da Silva marcos.pinheiro@unifesspa.edu.br
    Universidade Federal do Sul e Sudeste do Pará– Instituto de Estudos do Xingu, Faculdade de Ciências Agrárias
  • Kassiel Trajano da Luz kassiel.trajano@unifesspa.edu.br
    Universidade Federal do Sul e Sudeste do Pará– Instituto de Estudos do Xingu, Faculdade de Ciências Agrárias
  • Janismara Pereira Amorim janismaraamorim@unifesspa.edu.br
    Universidade Federal do Sul e Sudeste do Pará– Instituto de Estudos do Xingu, Faculdade de Ciências Agrárias
  • Eduardo Teixeira Neto eduneto19@unifesspa.edu.br
    Universidade Federal do Sul e Sudeste do Pará– Instituto de Estudos do Xingu, Faculdade de Ciências Agrárias
  • Marcello Matos dos Santos marcello.matos@unifesspa.edu.br
    Universidade Federal do Sul e Sudeste do Pará– Instituto de Estudos do Xingu, Faculdade de Ciências Agrárias

DOI:

10.34062/afs.v11i1.15658

Abstract

Anthropic activities that alter land cover patterns in Watersheds, such as deforestation, affect the food and sanitary security of the population. Thus, the objective of this study was to develop a quantitative analysis of the temporal evolution of deforestation in the Xingu River Watershed between the years 2008 and 2020. To achieve this, the methodology was organized into the following steps: Database construction (Xingu River Watershed boundaries, deforested areas, and Land Use and Land Cover); Data preprocessing; Analysis of the temporal evolution of deforestation; and Quantitative analysis of land cover change in the deforested areas. It became evident that deforestation did not exhibit a standardized behavior, due to the large proportion of deforested areas in 2008 and the abrupt reduction in 2012. Furthermore, the deforestation in 2012, 2016, and 2020 resulted in greater conversion of native forests into pasture than the regeneration of these areas. Therefore, it can be concluded that 2008 had the highest deforestation rate, due to the increase in soybean prices, and that 2012 had the lowest rates due to the implementation of environmental policies, highlighting the relationship between environmental policies and the seasonality of commodity prices with deforestation rates. It was also concluded that the main destination for the deforested areas has been pastureland for livestock, and a viable solution to identify and punish offenders, as well as support small-scale producers and recover areas devastated by deforestation, is land regularization.

Published

2024-06-12