Study Notes on Roads and Deforestation in Amazon
Roads and Deforestation in the Amazon: Overview and Findings
Authors: Christopher P. Barber, Mark A. Cochrane, Carlos M. Souza Jr., William F. Laurance
Institutions:
South Dakota State University
Instituto do Homem e Meio Ambiente da Amazônia (Imazon)
James Cook University
Article Information
History:
Received: 8 March 2014
Revised: 30 June 2014
Accepted: 6 July 2014
Available online: 1 August 2014
Keywords: Amazon, Roads, Protected areas, Conservation, Deforestation, Tropical forests
Abstract
Roads significantly impact deforestation in the Amazon.
The study assesses past deforestation relative to highway, river, and unofficial road networks.
Results indicate that deforestation occurs predominantly within 5.5 km of roads and 1 km of rivers: 95% of deforestation is within these proximities.
Protected areas (PAs) near roads and rivers show much lower deforestation rates (10.9%) compared to unprotected areas (43.6%).
Estimated deforestation avoided due to PAs: 39,462 km²; if PAs only displace deforestation, the estimate is 34,501 km².
Conclusion: Unofficial roads are critical drivers of deforestation; PAs reduce but do not fully prevent deforestation risk.
Introduction
The Brazilian Amazon contains a third of the world’s tropical forests, sustaining approximately 13% of global biodiversity (Lewinsohn and Prado, 2005).
Total area of moist tropical forests: ~4 million km²; 90% was formerly forested (Olson et al., 2001).
Deforestation rates: 0.52% per year (18,857 km² annually) during the 1990s and 2000s (INPE, 2009).
As of 2009, ~18% of forests converted to other land uses (Pereira et al., 2010).
Deforestation dynamics are most significant near transportation routes (Laurance et al., 2009; Alves, 2002 talks about 90% of deforestation near major roads).
Transportation Networks and Deforestation
Official Roads: 73,553 km in Brazilian Amazon, classified based on federal/state designations.
Unofficial Roads: Rapidly expanding in the Amazon, mostly for logging and colonization, leading to ecological degradation (Arima et al. 2005).
Reported new road growth of >40 km per 10,000 km² annually (Brandão and Souza, 2006).
Navigable Rivers: Another access mode contributing to deforestation, often neglected in analyses (Peres and Terborgh, 1995).
Protected Areas (PAs) in the Amazon
Established to conserve biodiversity and protect portions of the 23 Amazonian ecoregions (Rylands and Brandon, 2005).
By 2006, 1.8 million km² (45% of the Amazon) under some level of protection.
Types of PAs:
Strictly Protected Areas (19.2%): Aimed at biodiversity conservation.
Sustainable Use Areas (30.6%): Allow resource extraction.
Indigenous Reserves: Prevent large-scale deforestation.
PAs classified into two groups:
Threatened Lands: Actively resist development.
Remotely Located Lands: Defaultly protected due to lack of accessibility.
Studies indicate that PAs generally slow development pressure and deforestation (Barber et al., 2012; Nepstad et al., 2006).
Methods
Study Area
Spatial relationships examined between transportation networks and deforestation within the Brazilian Amazon.
Data Sources
Road/river datasets: From IBGE, included both official and unofficial roads contributing a total of 264,058 km networks for the study.
Land Cover Data: Provided by INPE PRODES project mapping Amazonian deforestation since 1997.
Transportation Network Influence
Used distances of 50 km and 100 km for highway evaluations based on past studies, with observed deforestation attributed to road proximity.
Effective distances for deforestation impacts calculated accurately (5.5 km for all roads, 1.0 km for navigable rivers).
Results
Deforestation Trends
By 2006, 476,925 km² of forest cleared in the Brazilian Amazon; 85.5% of cleared areas within 50 km of highways, increasing to 95.5% within 100 km.
Accessibility: 35.2% of the Amazon, encompassing 94.9% of deforestation.
Protected Areas Performance: 10.9% forest loss within PAs vs. 43.6% in unprotected lands.
Expected Deforrestation Scenarios in PAs
Prevention Scenario: Expectation of clearing due to accessibility similar to unprotected lands resulted in 61,792 km² potential clearing within PAs.
Displacement Scenario: Redistribution of expected deforestation across land types yielded 56,831 km² expected clearing, suggesting 34,500 km² would have been displaced from PAs to unprotected areas due to their protective status.
Discussion and Implications
Protected areas cannot fully insulate against deforestation risks; best practices involve managing accessibility and ongoing monitoring.
REDD+ initiatives can be effective if they recognize both deforestation prevention and displacement scenarios.
Careful governance of expanding road networks is critical to biodiversity conservation in the Amazon.
Conclusion
94.9% of deforestation linked to proximity to roads/rivers.
Less than 1.5% of protected forest cleared.
Significant reductions in deforestation rates in protected areas underscore their vital role in conservation efforts in accessible Amazonian regions.