Brazil’s Amazon rainforest is being rapidly degraded by logging and forest fires, as well as by droughts that are increasing under a changing climate that both favours forest fires and kills trees even without fire (Aleixo et al. Reference Aleixo, Norris, Hemerik, Barbosa, Prata, Costa and Poorter2019). Although deforestation is well known, greenhouse gas emissions from forest degradation are also very large, and in 2016 they accounted for 38% of the total forest carbon loss in the Brazilian Amazon (Walker et al. Reference Walker, Gorelik, Baccini, Aragon-Osejo, Josse and Meyer2020). The southern and eastern edges of the Brazilian Amazon is already heavily deforested and degraded (Fearnside Reference Fearnside and Shugart2017), but in the western portion of the region the forest is still almost entirely intact. However, forest degradation is shifting to the western portion of the Brazilian Amazon (Matricardi et al. Reference Matricardi, Skole, Costa, Pedlowski, Samek and Miguel2020), which includes the area impacted by Highway BR-319. Here, we present evidence of forest degradation associated with illegal logging and mining in the highway’s ‘middle section’ (Supplementary Appendix S1, available online), indicating the lack of governance even before the area has experienced the increased pressures that would result from reconstructing BR-319.
BR-319 was built in 1972/1973 and officially inaugurated in 1976, but the road was abandoned by the Ministry of Transport in 1988 due to its lack of economic viability. Today, the proposed reconstruction of BR-319 is one of the Brazilian government’s priority projects (Ferrante & Fearnside Reference Ferrante and Fearnside2019). With the BR-319 reconstruction and the opening of the planned roads that would branch off from this highway, the deforested area has been projected to increase by over 1200% by 2100 as compared to the area that had been cleared by 2011 (dos Santos Junior et al. Reference dos Santos Junior, Yanai, Sousa Junior, de Freitas, Pinheiro and de Oliveira2018).
Fifteen years ago, the danger of unrealistic ‘governance scenarios’ for Brazil’s proposed Amazonian highways was highlighted (Fearnside Reference Fearnside2006). Since then, the assertions by highway proponents that the severe environmental and social impacts of these infrastructure projects would be avoided because government agencies and/or non-governmental organizations would bring governance and sustainable development to the affected areas have repeatedly proven to be false (e.g., Fearnside Reference Fearnside, van der Ree, Smith and Grilo2015). Despite the legal inconsistencies (Appendix S1), Brazil is now set to embark on what is probably the most consequential of all of its many Amazonian plans: the reconstruction of Highway BR-319.
Illegal logging
We made observations on BR-319 in two research modules of the Biodiversity Research Program of Brazil’s National Institute for Research in Amazonia (PPBio/INPA) at 10 points experiencing forest degradation from logging (Fig. 1(a)). We observed disturbances in these plots such as drag trails, uprooted trees, damaged tree crowns and clearings, as well as log-storage decks, tree stumps left from logging and trees marked for cutting in the near future (Fig. 1(b)). The logging does not comply with the procedures and parameters for legal forest-management projects (Brazil, MMA 2009).
(a) Map of Highway BR-319 and the location of illegal logging and mining documented here; (b) an illegally cut log; (c) a log-storage deck; and (d) a pit dug by gold prospectors.
These logging areas show no signs of the required directed-felling techniques that avoid knocking down trees that are either not planned for harvesting or that are protected by law, nor are the logging trails and roads planned. The required planning of trails and roads in legal management projects is designed to reduce the impact of soil compaction that can last for decades (Dearmond et al. Reference Dearmond, Emmert, José, Lima and Higuchi2019). The stumps and logs we observed did not have tags, which are required to allow later identification of the origin of the wood.
Vila Realidade, a vila (town) near the southern end of the highway stretch to be reconstructed, sprung up with the arrival of two busloads of organized sem-terras (landless farmers) in c. 2004 (Fearnside & Graça Reference Fearnside and Graça2006). A continuous flow of individual posseiros (squatters) subsequently expanded the occupation of the surrounding land and increased the population of the town. Occupied government land surrounding the town has been legalized as an official settlement project, and the area has been designated as a ‘district’ in the municipality (county) of Humaitá. An audit of the BR-319 ‘maintenance’ project by the Federal Audit Court highlighted the Realidade area as a new frontier for logging, with a large amount of illegal logging and unauthorized transport of logs, according to information from the Brazilian Institute for the Environment and Renewable Natural Resources (IBAMA) and the Chico Mendes Institute for Biodiversity (ICMbio) (Brazil, TCU 2020).
In 2018, migrants who settled along BR-319 in the Realidade district were interviewed by the Folha de São Paulo newspaper. One of the migrants indicated that, in addition to livestock, he had a forest-management project with a licence issued by the environmental agency of the state government of Amazonas (IPAAM) and that he did not have a land title (Appendix S1). This implies that IPAAM violated Brazilian regulations that require proof of land ownership as a precondition for approving forest-management plans (Brazil, MMA 2006). We also found areas with forest-management licences granted by IPAAM along BR-319 that did not have a Rural Environmental Registry (CAR; Cadastro Ambiental Rural, the registry of rural properties in Brazil) entry, which is also mandatory for forest management (IPAAM 2011).
Forest management in the Brazilian Amazon often serves as a form of subterfuge that allows illegally harvested timber to appear legal through the practice known as ‘heating up wood’, where wood from illegal logging is camouflaged as volume credits from legal forest management (Brancalion et al. Reference Brancalion, de Almeida, Vidal, Molin, Sontag, Souza and Schulze2018). This is easier if the locations are in close proximity, and IPAAM’s public data indicate forest-management plans approved by the agency less than 20 km from the points of illegal logging visited in the present study.
The fact that the areas of logging authorized by IPAAM do not have land titles and CARs and are close to the areas of illegal logging brings into question the legitimacy of the timber industry. In view of national and global concerns regarding climate mitigation, it is essential that the economic activities in the area that is being opened to exploitation by BR-319 comply with environmental laws that are intended to keep forest standing and healthy over the long term. For this to occur, it is necessary that government authorities certify that legal requirements are met. Otherwise, the approval of forest management will continue to function as an engine for degradation through predatory logging. Greater enforcement is needed if legal timber industries are to be financially sustainable, since illegal activity competes unfairly in the market with legal forest management.
Illegal mining
Mining poses significant risks to Brazil’s Amazonian forests (Sonter et al. Reference Sonter, Herrera, Barrett, Galford, Moran and Soares-Filho2017). The current president of Brazil has encouraged both corporate mining projects and garimpeiros (‘wildcat miners’) in the Amazon region, including those invading indigenous lands, thereby increasing land conflicts and forest destruction (Ferrante & Fearnside Reference Ferrante and Fearnside2019, Reference Ferrante and Fearnside2020). At the president’s request, the Ministry of the Environment has punished IBAMA officials and inspectors for carrying out repression measures on illegal mining in indigenous land (Appendix S1). In the present study, we observed exploratory ore pits at 3 of the 10 sampled points (Fig. 1(c)) – these are pits that are dug to evaluate the mineral potential of the site. The agency responsible for granting, storing and managing data and information on any mining and prospecting activity is the National Mining Agency (Brazil, PR 2017). However, no records of the points we observed are contained in the agency’s Geographic Mining Information System (Brazil, ANM 2020). The presence of exploratory pits indicates a plan to intensify mining activity by illegal actors. Given the ongoing dismantling of the country’s environmental inspection agencies by the federal government, mining activities have increasingly become a risk to the environment in Brazilian Amazonia and to the region’s traditional peoples (Ferrante & Fearnside Reference Ferrante and Fearnside2019). This is particularly worrisome along BR-319 because gold miners in Humaitá (with the help of local politicians) set fire to the offices of IBAMA and ICMbio in 2018 (Appendix S1), once again showing a total lack of governance in this part of Amazonia.
Conclusion
We present evidence that Highway BR-319 in its current state is already leading to forest degradation along its route and that governance in the area is essentially non-existent. Under these circumstances, the reconstruction of BR-319 and the building of planned connecting roads would act as spearheads for deforestation and forest degradation in the western portion of the Brazilian Amazon. The proposed reconstruction project should not be approved until governance is in fact established both in the area along the highway route and in the other areas to which migration would flow. This process will take years and will require fundamental changes in the control of activities such as logging and mining, as well as addressing the underlying issues that lead to deforestation and forest degradation when Amazonian highways are built.
Supplementary material
To view supplementary material for this article, please visit https://doi.org/10.1017/S0376892921000084
Acknowledgements
We acknowledge the support of the National Institute for Research in Amazonia (INPA) through its Brazilian Biodiversity Research Program (PPBio) and the National Institute for Amazonian Biodiversity Research (CENBAM). We thank the Brazilian Biodiversity Research Program (PPBio) for the logistical support at the research modules.
Financial support
The authors’ research is funded only by academic sources. MBTA and LF thank the National Council for Scientific and Technological Development (CNPq). PMF thanks CNPq (429795/2016-5, 610042/2009-2, 311103/2015-4), Amazonas State Research Support Foundation (FAPEAM) (708,565) and the National Institute for Research in Amazonia (INPA) (PRJ13.03).
Conflict of interest
None.
Ethical standards
None
