Brazilian Amazon The Millennium Ecosystem Assessment MEA

2.2.3. Brazilian Amazon

The impact of interregional drivers on land use change, especially in the Brazilian Amazon, is considered in several other works, and the historical evolution of scenarios proposed hardly represents the actual situation of deforestation reduction since 2004. This does not invalidate the proposed models by different authors, or the potential future scenarios described in each study, as policy regulation may lose its current presence and strength. Scenarios proposed by Laurance et al. 2001 focus on the discussion on the effects of Avança Brasil Program Brasil, 1999, a National economic development plan proposed by the Brazilian Government over the years 2000-2007, in which several infrastructure projects in the Amazon were included. To calculate the impacts of new highways, railroads, gas pipelines, hydroelectric projects, power lines and river-channelization projects described in the development program, Laurence et al., 1999 developed two scenarios for the future of Brazilian Amazon for the following twenty years. They considered two scenarios, a “pessimistic”, which followed the deforestation rate at that time, and an “optimistic”, where deforestation and forest degradation were reduced by several protection strategies. In both scenarios, the results show enormous changes in Amazon land cover, especially in the “pessimistic”, where few areas of original forest remain Figure 6, Table 5. Figure 6. The future of the Brazilian Amazon for two different scenarios by the year 2020 Laurence et al., 2001. Scenarios a optimistic and b pessimistic. Areas in black show deforested or heavily degraded regions, red shows moderately degraded, yellow lightly degraded and green is pristine Table 5. Predicted rates of deforestation and degradation Laurence, 2001 Optimistic scenario Pessimist scenario Deforestation 2,690 Km 2 per year 5,060 Km 2 per year Degraded moderately or heavily 15,300 Km 2 per year 23,700 Km 2 per year The contribution of protected areas to possible reductions in deforestation is addressed in Soares-Filho et al. 2010. In this work five scenarios for 2050 that consider the importance of protected areas were developed for the Brazilian Amazon: i exclusion of all current protected areas, ii all protected areas created until 2002 iii protected areas established by 2008, except for 13 areas established in the 2003-2008 ARPA Amazon Protected Area Program, iv protected areas created until 2008, v protected areas created until 2002 plus expansion underway with the support of the ARPA program. These land cover scenarios with different distributions of protected areas were combined with two socioeconomic scenarios: high and moderate agricultural growth. The first LUC scenario, with the drastic exclusion of all protected areas, produced a higher risk map of deforestation in those areas, and the other four scenarios depict the progressive contribution of protected areas to a reduction in deforestation. Figure 7 shows the results of deforestation and emissions for each of the protected areas scenarios. Figure 7. Deforestation and carbon emissions in the Brazilian Amazon biome: average of two socioeconomic scenarios with four protected areas scenarios Soares-Filho et al. 2010. The scenarios described in the studies by Laurence et al. 1999 and Soares- Filho et al. 2010 [and references therein], highlight the importance of infrastructure projects and protected areas for the landscape dynamics in the Amazon. Nevertheless, other internal and external factors also modulate and regulate land use change and must be considered. For example, a recent study by the Brazilian Agriculture Ministry Brasil, 2012, which projected scenarios for Brazilian agro-business for 2022, shows an expressive increase in agriculture production in the next years, with expected growth in internal and external demand. This study projects an increase of 70,000km 2 in crop production area, mainly concentrated in beans 47,000km 2 and sugarcane 19,000km 2 . Considering these numbers, the pressure over forest areas could be enhanced. Aguiar 2006 advances beyond intraregional drivers by also considering accessibility to markets and uses a dynamic spatial model to build different exploration scenarios of LUCC until 2020. The scenarios proposed by Aguiar 2006, detailed in Table 6, highlight the importance of differences in market accessibility on determining drivers of land use change in the Brazilian Amazon. The main conclusions drawn from these scenarios were: a connection to national markets is the most important factor for capturing the spatial patterns of the new Amazonian deforestation frontiers; b intraregional dynamics are influenced by the interaction between connectivity e.g. to local and national markets and other factors e.g. economic attractiveness, agrarian structure, environmental, where the importance of determining factors vary across the Amazonia; c these differences led to heterogeneous impact of policies such as road paving, creation of protected areas, law enforcement across the region. Together, the results of the five explorative scenarios presented in Table 6 are complementary, helping to draw different aspects of the occupation process in the Brazilian Amazon. Table 6. Scenario exploration summary of the LUCC adapted by Aguiar, 2006 Exploration Description Model Scenarios Allocation Demand Law enforcement Alternative factors: Accessibility In this exploration, the focus is on connectivity factors. Considering Roads No Change Baseline No Considering Roads No Change Baseline No Considering Roads No Change Baseline No Alternative factor: Local markets The focus here is on accessibility to local markets. Considering Roads No Change Baseline No Considering Urban centers No Change Baseline No Policy analysis: road paving and protected areas Here the public policies that influence intraregional conditions for agricultural use, such as road paving Considering Roads Paving and protection Baseline No Considering Urban centers Paving and protection Baseline No and the creation of protected areas, are considered Policy analysis: Law enforcements Law enforcement policies, such as deforestation limits inside private properties, are considered Considering Roads No Change Baseline Private reserves 50 local command and control Considering Roads No Change Baseline Market constraints Analyzes scenarios of increasing and decreasing demand for land in Amazonia, corresponding to higher or lower pressure for forest conversion determined by national and international agribusiness. Considering Roads Paving and protection Decrease No Considering Roads Paving and protection Increase No Considering Urban centers Paving and protection Decrease No Considering Urban centers Paving and protection Increase No To investigate the impacts of biofuels production, in Southeast and Central regions of Brazil, and its cascade effects over agricultural and cattle ranching frontiers Lapola et al. 2010 focused on market pressure for land use scenarios until 2020. The direct and indirect land use changes in scenarios with and without biofuel expansion were then analysed. Lapola et al. suggested a displacement of pastureland and cattle production towards the Brazilian Amazon, showing an expansion of 121,970 km 2 into the region. Figure 8, extracted from this work, presents the difference between land use maps with and without the expansion of biofuel plantations in 2020. Figure 8. Indirect land use changes caused by the fulfillment of Brazils biofuels production targets to 2020 adapted by Lapola et al. 2010.

2.2.4. National Level