The Brazilian Amazon is one of the world’s largest rainforest regions and plays a key role in biodiversity conservation, maintenance of ecosystem services, and storage of terrestrial carbon stocks (Laurance et al., 2001). In recent years, many advances have been made in combating the widespread and illegal use of the region’s natural resources. Political actions based on the establishment of new protected areas (PAs), increases in law enforcement, and support for forest-based economic activities have resulted in a significant deforestation reduction in the region (Fearnside, 2005; Nepstad et al., 2009; Silva, Rylands & Da Fonseca, 2005). In 2010, an extensive network of PAs protected about 54% of the remaining forests of the Brazilian Amazon and contained around 56% of its forest carbon (Soares-Filho et al., 2010).
The creation and maintenance of PAs is the most effective way to protect vast areas of tropical forests in the Brazilian Amazon (Dalla-Nora et al., 2014; Soares-Filho et al., 2010; Soares-Filho et al., 2006). Recent studies have indicated that PAs can reduce deforestation and pave the way to a more sustainable use of the region’s natural resources (Barber et al., 2012; Nepstad et al., 2014; Nepstad et al., 2006; Nepstad et al., 2009; Pfaff et al., 2015). However, despite all these recent efforts, natural resource degradation in the Brazilian Amazon is still pervasive and thus PAs are subjected to several pressures and threats. Four major factors determine the intensity of pressures on a PA: (a) accessibility; (b) local human population density; (c) management category; and (d) age of the PA.
Accessibility of PAs can be measured by evaluation of navigable rivers and roads that cross or form the boundaries of a given reserve (Peres & Terborgh, 1995). Peres & Lake (2003) estimate that much of the Amazon basin in Brazil can be accessed on foot from the nearest river or functional road and found that the density of preferred hunted species tended to decrease in areas closer to access points (e.g., roads, rivers). In Amazonia, until 1997, about 90% of deforestation was concentrated in areas within 100 km of main roads established by federal government development programs (Alves, 2002).
In tropical forests, a positive relationship is observed between the increase in both human population and natural resource extraction, and deforestation (Laurance et al., 2002; Lopez-Carr & Burgdorfer, 2013; Lopez-Carr, Lopez & Bilsborrow, 2009). However, in the Brazilian Amazon, this relationship is not always positive. While in some regions population density is not a direct cause of deforestation, in others it may be one of the leading causes (Jusys, 2016; Tritsch & Le Tourneau, 2016).
The age of the PA (or the time since its creation) is often correlated with better conservation results. Assessments in marine reserves reveal that areas that have been protected for longer show an increase in the quantity and richness of fish species (Claudet et al., 2008; Molloy, McLean & Côté, 2009). However, the relationship of PA age with conservation results may be antagonistic, with some younger PAs in the Brazilian Amazon obtaining better results in relation to reduction or avoidance of deforestation compared with older PAs (Soares-Filho et al., 2010).
The classification of PA classes according to the International Union for Conservation of Nature (IUCN) criteria (Dudley, 2008), into strictly protected (I–IV) and sustainable use (or multiple use) management classes (V–VI), has generated several discussions on the efficiency of one category or another in reducing the illegal use of natural resources (Nelson & Chomitz, 2011). While some experts do not believe in the efficiency of multiple-use PAs in conserving biodiversity in the long term, others believe adoption of this class of PA will lead to a more effective and inclusive conservation strategy (De Toledo et al., 2017; Schwartzman et al., 2010).
Laurance et al. (2012) identified that in addition to the deforestation, across all three tropical continents, logging, wildfires, and overharvesting (hunting and harvest of non-timber forest products) are major threats to tropical PA integrity. Many of these threats, unlike deforestation, are difficult to detect (e.g., surface fire, small-scale gold mining, selective logging) or undetectable (e.g., hunting and exploitation of animal products and extraction of non-timber plant products) even with increasingly sophisticated remote sensing techniques (Peres, Barlow & Laurance, 2006). In this sense, on the ground enforcement activities can result in a wealth of information about the magnitude and types of illegal activities occurring within PAs (Gavin, Solomon & Blank, 2010) that are not detected by commonly used remote sensing techniques.
In this study, we evaluated the illegal use of natural resources within 118 federal PAs in the Brazilian Amazon, through the analysis of 4,243 illegal activities (infraction records) obtained from law enforcement activities in the period of 2010–2015. First, we categorized illegal activities to determine the main threats found within PAs. Then, we used the infraction records to evaluate the following hypotheses about the intensity of pressures on PAs from illegal activities: (a) fewer illegal activities occur in sustainable use PAs because they have fewer use restrictions than PAs under integral protection; (b) fewer illegal activities occur in older PAs because they have better established administrative structures and management than newer ones; (c) PAs with higher local population density tend to have more illegal activities because of greater anthropogenic pressure; and (d) PAs with greater accessibility tend to have more illegal activities.
Materials & Methods
The data used as explanatory variables were obtained from the following publicly available sources: a shapefile describing the geographic boundaries of the Amazon biome from Ministério do Meio Ambiente (MMA, 2016); a shapefile describing the geographic boundaries of federal PAs (conservation units) from Instituto Chico Mendes de Conservação da Biodiversidade (ICMBio, 2016b); shapefiles describing water bodies (water masses) and rivers (multiscale ottocoded hydrographic base 2013) from Agência Nacional de Águas (ANA, 2013); a shapefile describing roads at 1:250,000, and limits of Brazil and South America from Instituto Brasileiro de Geografia e Estatística (IBGE) (IBGE/DGC, 2015); and shapefiles describing the populational “grid” of Brazil from IBGE (IBGE, 2016a).
The data on illegal use of natural resources (illegal activities) used were standardized and made available to authors by the Instituto Chico Mendes de Conservação da Biodiversidade/Divisão de Informação e Monitoramento Ambiental (ICMBio/DMIF, 2017, unpublished data; available upon request from ICMBio: http://www.icmbio.gov.br/portal/). The maps presented in this study (Fig. 1, Figs. S1 and S2) and area calculations were produced in an equal area projection (Projection: Albers Equal Area Conic; Datum: South America 1969). The geographic information system (GIS) environment was created and the elaboration of spatial variables performed based on geographic data obtained from official sources, in ArcGIS 10.2 software (ESRI, Redlands, CA, USA). The data on illegal activities compiled and formatted for our study are available in Data S1.
We delimited the Brazilian Amazon (Fig. 1) according to the boundaries of the Amazonia biome as defined by the Instituto Brasileiro de Geografia e Estatística (IBGE, 2004). The IBGE’s proposal follows the boundaries laid out in the original extension of the tropical rainforests of northern Brazil (Góes Filho & Veloso, 1982), which is inside the tropical moist broadleaf forests biome (Olson et al., 2001). The Brazilian Amazon covers an area of around 4.3 million km2, about 50% of the of the country’s territory. The region has a population of roughly 21.6 million people, 72% of whom live in cities in nine Brazilian states (Amazonas, Acre, Rondônia, Roraima, Amapá, Pará, Mato Grosso, Maranhão, and Tocantins) (Silva, Prasad & Diniz-Filho, 2017).
Federal protected areas
We evaluated 118 federal PAs established before 2010 in the Brazilian Amazon, totaling an area of around 600,000 km2 (Fig. 1, Table 1, Table S1). Of these 118 PAs, 38 are strictly protected (Biological Reserve (Rebio), n = 9, IUCN Ia; Ecological Station (Esec), n = 10, IUCN Ia; and National Park (Parna), n = 19, IUCN II), and 80 are sustainable use (Area of Relevant Ecological Interest (Arie), n = 3, IUCN IV; Environmental Protection Area (Apa), n = 2, IUCN V; National Forest (Flona), n = 32, IUCN VI; Sustainable Development Reserve (RDS), n = 1, IUCN VI; and Extractive Reserve (Resex), n = 42, IUCN VI). Although fewer strictly protected than sustainable use reserves were analyzed, these two major classes of PA have similar total areas (strictly protected: roughly 295,000 km2 and sustainable use: roughly 305,000 km2). In total, we studied 91.5% of the PAs managed by the federal government in Amazonia, which corresponds roughly 76% of the total territory in federal PAs. Overall, Brazil have 789,280 km2 distributed in 326 PAs managed by the federal government across the country and 127 PAs in Amazonia (ICMBio, 2016a).
|Protected area class||Protected area category||IUCN||PAs (n)||Area (km2)||Illegal activities (n)||Fines (U$)a|
|Strictly protected||Ecological Station||Ia||10||55,248.94||257||27,594,947.29|
|Sustainable use||Relevant Ecological Interest Area||IV||3||189.31||6||13,573.23|
|Environmental Protection Area||V||2||20,632.85||5||384,154.04|
|Sustainable Development Reserve||VI||1||644.42||3||10,782.83|
All PAs are forested, with a few also featuring grasslands and savannas. Thirteen PAs are coastal/marine reserves. We excluded nine areas established after 2010, because we analyzed the period of illegal activity spanning from 2010 to 2015. In our study, only PAs (conservation unities) managed by the federal government under the Brazilian System of Conservation Units (SNUC) (Brasil, 2000) were evaluated. Therefore, for the purpose of this study, we excluded state, municipal and private areas, as well as indigenous lands and quilombola lands (traditional Afro-Brazilian communal territories).
Illegal use of natural resources
Official figures for illegal use of natural resources (hereafter illegal activities) within federal PAs in the Brazilian Amazon were obtained by analysis of 4,243 environmental infraction records (Data S1, Table S1). Irregularities are framed according to Federal Decree 6514 (2008), which deals with administrative environmental infractions and penalties (Brasil, 2008). For analytical purposes, we considered that each environmental infraction corresponded to an illegal activity.
Due to the large number of types of infraction and considering that the categories presented by the Brazilian Decree are very broad (e.g., hunting and fishing would fall into the same category), a new categorization of illegal activities was proposed. We considered the infraction framework, the number of occurrences of each type of infraction, and the main characteristics of illegal activities (Fig. 2, Table S2).
Protected area accessibility
We defined accessibility (or accessible area) of PAs as the intersection between the total area of a PA with the area of a 10 km buffer adjacent to roads and rivers located within or outside PAs. The definition of accessibility within 10 km of rivers and roads takes into consideration that most natural resource exploitation in the Amazon is limited by transportation. Preliminary work conducted in Amazonia suggested that 10 km is the maximum distance local people can travel in order to collect non-timber forest resources and/or hunt (Peres & Lake, 2003; Peres & Terborgh, 1995).
To measure accessibility (Fig. S1, Table S2), we used the following procedures: creation of 10 km buffers around roads and rivers; union of the files produced when applying 10 km buffers; intersection of buffers and PAs (accessibility or accessible area); calculation of the accessible area (km2); and division of the accessible area by the total area of the PA. All roads mapped by the IBGE at 1:250000 were considered (IBGE/DGC, 2015). Selection of the main rivers was carried out according to the criteria adopted by the National Water Agency for the characterization of Brazilian rivers, in which main rivers are drainage sections with an area of contribution greater than 20,000 km2.
Population density was considered at a distance of 50 km around the PAs. Population density information was obtained from the “Brazilian statistical grid” (IBGE, 2016a; IBGE, 2016b) prepared by IBGE based on the Brazilian population census of 2010 (IBGE, 2010; IBGE, 2011). The “Brazilian statistical grid” contains the amount of the Brazilian population in georeferenced polygons from 1 km2 in rural areas and polygons up to 200 m2 in urban areas. The grid is more refined than the municipal level data, which is generally used in studies that analyze demographic and socioeconomic factors for the Brazilian Amazon. For visualization purposes, we elaborated a population density map of the Amazon biome from the “Brazilian statistical grid” (Fig. S2).
In order to produce the population density variable (Table S2) in the area surrounding the PAs, we first created a 50 km buffer from the perimeter of each PA; then intersected the 50 km buffer area of each PA with the “Brazilian statistical grid”; and finally divided the population within the buffer area of 50 km by its area (km2). Areas located outside the Brazilian territory and in marine areas were excluded. When PAs were located very close to the border of the Amazon biome, a 50 km band was considered beyond the limits of the biome, but within Brazilian territory.
A summary of all environmental infractions in the period from 2010 to 2015 allowed assessment of the main illegal uses of natural resources (by verifying the illegal activities that generated the infraction notices), as well as the categorization of these illegal uses (Fig. 2). The temporal trend of the illegal use of natural resources for the study period was evaluated using a linear regression. The total number of illegal activities was also summarized for each PA (Table S1), in relation to management categories (strictly protected and sustainable use) (Table 1). For further analysis, the three categories of illegal activities with the highest number of records and their totals summarized for each PA were used. In order to take in to account differences in the area of PAs and to standardize our variables, the total number of infractions and the total number of the three most common infraction categories were divided by the number of years (n = 6) and the area of the PA (km2). This procedure was performed considering that the PAs have varied sizes and the measure of law enforcement effort that we adopted was the number of infraction records per year.
In order to normalize the data, transformations were applied to the following variables: illegal activities =log10 ((illegal activities ×105) +1); age =log10 protected area age; accessibility ; and population density =log10 (population density × 105).
We used Spearman correlation analysis to evaluate the independence between our environmental variables (Table S3). Variables with weak correlations (rs < 0.50) were retained for use in subsequent analyses. The differences in the influence of management classes of PAs (sustainable use or strictly protected), age, accessibility, and population density, on illegal activities occurring in PAs, were analyzed using generalized additive models (GAMs, Gaussian distribution family) (Guisan, Edwards & Hastie, 2002; Heegaard, 2002; Wood, 2017). GAMs were run separately for each of the three most recorded illegal activities. In order to verify possible differences in the number of illegal activities in stryctly terrestrial PAs (n = 105) and coastal/marines (n = 13) ones, we used a Mann–Whitney U test. All analyses were performed in the R environment for statistical computing (R Development Core Team, 2016).
Federal protected areas and illegal use of natural resources
Of the 118 PAs evaluated, 107 had at least one infraction reported between 2010 and 2015; only 11 had no records of illegal activities (Fig. 1, Table S1). Overall, there was a decrease in the number of illegal activities within federal protected areas in the Brazilian Amazon for the study period (R2 = 0.56, p = 0.09). A total of 4,243 occurrences of illegal use of natural resources were evaluated, and these resulted in total fines of US$224,646,139.84 (Table 1). Strictly protected PAs had a relatively higher total fines value (US$143,948,856.38) compared to that of sustainable use reserves (US$80,697,283.46). Similarly, strictly protected PAs presented slightly higher numbers of illegal activities (n = 2, 179) than sustainable use reserves (n = 2, 064). The mean number of total illegal activities in each PA was 35 (median 19.50), with 50% of PAs within the range of 8.0 to 47.5. The ten PAs with the highest frequency of illegal activities were Rebio do Abufari (n = 316), Parna Serra do Divisor (n = 199), Parna Mapinguari (n = 187), Rebio do Jaru (n = 158), Rebio do Gurupi (n = 137), Resex Marinha de Soure (n = 129), Parna do Cabo Orange (n = 122), Rebio Trombetas (n = 122), Flona do Jamaxim (n = 97), and Resex Chico Mendes (n = 93).
We found 27 types of illegal uses of natural resources that were grouped into 10 categories of illegal activities (Fig. 2, Table S2). The most commonly registered infractions were related to suppression and degradation of vegetation (37.36%), followed by illegal fishing (27.34%) and hunting activities (18.15%). These three categories together corresponded to 82.85% of all records of illegal activities in the entire study period. Infractions related to the suppression and degradation of vegetation were responsible for the highest total amount of fines among the 10 categories of illegal activities, US$188,337,814.39, which corresponds to around 83% of all fines imposed in the study period. The four PAs with the highest number of illegal activities related to the suppression and degradation of vegetation were the Parna Serra do Divisor (n = 109), Rebio do Gurupi (n = 94), Parna Mapinguari (n = 92), and Resex Chico Mendes (n = 71). For illegal fishing, the Rebio do Abufari (n = 168), the Parna do Cabo Orange (n = 120), the Rebio Jaru (n = 89), and the Esec Maracá (n = 52), had the highest number of infractions. Regarding hunting, the four reserves with the majority of records were the Rebio do Abufari (n = 168), the Parna Serra do Divisor (n = 72), the Rebio Trombetas (n = 46), and the Flona Tefé (n = 35).
Predictors of illegal activities within federal protected areas
The mean age of federal PAs in the Brazilian Amazon (calculated from 2015) was 18.92 years (median = 14, range = 6–54 years), with 50% of reserves ranging in age from 10 to 26 years. The total mean area of the PAs was 5,092.66 km2 (median = 2,858.73 km2). The reserves ranging from 1,209.90 to 6,813.01 km2 in a 50 km buffer population density around PAs averaged 7.49 inhabitants per km2 (median = 1.54 inhabitants/km2), with 50% of the PAs ranging from 0.63 to 4.68 inhabitants per km2. The protected area with the lowest population density in the surroundings was the Resex do Xingu with 0.06 inhabitants/km2 and the highest density was found in the neighborhood of Parna Anavilhanas with 75.90 inhabitants/km2. The overall index of accessibility was on average 43% (median = 33%), and 50% of PAs had accessibility between 15% and 68%. Regarding accessibility, it is important to highlight that 17 PAs presented 100% of this variable, as well as 10 PAs had zero accessibility (Table S1).
The explanatory power of the GAMs was low for all groups (Table 2), with a maximum explained variation of 41.20% (R2 adjusted = 0.39) for total illegal activities, and a minimum of 14.6% (R2 adjusted 0.12) for illegal hunting activities. From all explanatory variables analyzed in our study, population density was the most important predictor of total number of infractions (Fig. 3), as well as illegal fishing, suppression and degradation of vegetation, and hunting. The second most important predictor of illegal activities was accessibility, which was positively related to all illegal activities (Fig. 4) and to illegal fishing. PA classification was only an important predictor for illegal fishing, with sustainable use PAs having lower levels of illegal fishing. The age of a PA was not a significant predictor for any of the illegal activities analyzed in our study.
|All illegal activitiesa||Hunting activitiesb||Illegal fishingc||Vegetation degradationd|
|Slope (SE)e||t value||Slope (SE)e||t value||Slope (SE)e||t value||Slope (SE)e||t value|
|Intercept||−1.460 (0.521)||−2.80***||−0.909 (0.577)||−1.57||−1.718 (0.643)||−2.67***||−1.318(0.618)||−2.13**|
|Classesf (Sustainable use)||−0.160 (0.159)||−1.00||−0.198 (0.176)||−1.12||−0.476 (0.197)||−2.42**||0.163 (0.189)||0.86|
|Ageg||−0.005 (0.007)||−0.67||0.002 (0.008)||0.29||−0.005 (0.009)||−0.53||−0.009 (0.009)||−1.02|
|Accessibilityh||0.968 (0.256)||3.85****||0.502 (0.284)||1.77*||0.899 (0.316)||2.84***||0.527 (0.304)||1.73*|
|Population densityi||0.574 (0.112)||5.14****||0.317 (0.124)||2.56**||0.508 (0.138)||3.68****||0.449 (0.133)||3.39****|
|Model deviance explained (%)k||41.20||14.60||27.30||22.10|
In relation to the number of illegal activities and the PA location (coastal/marine or terrestrial), we found a significant decrease in the number of all illegal activities (p < 0.001) and a significant increase in the number of illegal fishing (p < 0.001) in coastal/marine PAs (Table S4). Illegal activities related with hunting and vegetation degradation were not significantly different in these two locations of PAs.
Globally, the illegal use of natural resources is one of the biggest threats to biodiversity, and generally threatens the integrity of PAs and the viability of endangered species (Conteh, Gavin & Solomon, 2015; Dinerstein et al., 2007; Gavin, Solomon & Blank, 2010; Laurance et al., 2012). Despite the fact that Amazonian PAs are one of the most important means of reducing deforestation rates in the biome (Kere et al., 2017), PA creation alone is not sufficient to reduce threats to biological diversity.
Our analysis showed that there was a wide range of illegal activities that threatens the biodiversity of Amazonian federal PAs. We found that illegal activities related to suppression and degradation of vegetation, illegal fishing and hunting activities were the most commonly recorded. These three activities have been highlighted in several assessments of biodiversity threats globally: hunting and the illegal wildlife trade (Dudley, Stolton & Elliott, 2013; Nijman, 2015; Sharma et al., 2014; Tella & Hiraldo, 2014; Underwood, Burn & Milliken, 2013); fishing in prohibited locations, outside permitted periods and in excess of established quantities or sizes (Free, Jensen & Mendsaikhan, 2015; Sethi & Hilborn, 2008; Thomas, Gavin & Milfont, 2015); and illegal logging, deforestation and degradation of vegetation (Chicas et al., 2017; Curran et al., 2004; Funi & Paese, 2012; Yonariza & Webb, 2007). Although illegal activities related to the suppression and degradation of vegetation, illegal fishing, and poaching activities were those most frequently recorded in Amazonian PAs, it does not mean that other less prominent illegal activities are not of concern.
The population density surrounding PAs was the most important variable in our study, predicting total illegal activities, as well as the suppression and degradation of vegetation, illegal fishing, and poaching activities. This finding is in line with the results of other tropical forest studies that have observed a positive relationship between the growth of human populations and an increase in natural resource extraction and deforestation (Geist & Lambin, 2002; Laurance, Sayer & Cassman, 2014; Lewis, Edwards & Galbraith, 2015; Lopez-Carr & Burgdorfer, 2013; Marques, Schneider & Peres, 2016).
We found that accessibility was positively related only with the total number of illegal activities and to illegal fishing, while for hunting activities and vegetation suppression and degradation activities this variable was marginally significant. Despite this, it was possible to verify the importance of accessibility in predicting illegal activities within PAs. Roads and highways have a fundamental role in opening the tropics to destructive colonization and exploitation (Laurance et al., 2001). Roads provide access and dispersion of people within tropical forests and facilitate access for hunters, miners, land speculators, and others into forest core areas (Laurance, Goosem & Laurance, 2009). For example, the increasing deforestation of the Brazilian Amazon began with the construction of the Belém-Brasília highway in the 1960s (Vieira et al., 2008) and the opening of the Transamazon Highway in 1970 (Fearnside, 2005). Barber et al. (2014) observed that until 2006, deforestation in the Brazilian Amazon was higher in areas closer to roads and rivers, with almost 95% of the total deforested area within 5.5 km of roads and up to 1 km from rivers. Recent studies show that populations of aquatic species (e.g., giant otters, alligators) in more accessible areas have collapsed throughout the Amazon basin (Antunes et al., 2016).
We found no relationship between the age of PAs and illegal activities, although the age of a PA is often correlated with conservation results (Claudet et al., 2008; Molloy, McLean & Côté, 2009; Soares-Filho et al., 2010). Our results show that sustainable use PAs decrease the frequency of illegal fishing activities. This relationship can be attributed to the fact that residents of the reserves assist surveillance. Nepstad et al. (2006) verified that sustainable use PAs and indigenous lands hold great importance for the prevention of deforestation and wildfires. This pattern was also observed in a global analysis of the effectiveness of strictly protected and sustainable use PAs in reducing tropical forest fires, where sustainable use PAs were more efficient (Nelson & Chomitz, 2011). Porter-Bolland et al. (2012) observed that forests managed by communities presented lower and less variable deforestation rates across the tropics. These findings reinforce the idea that in order to achieve an effective conservation, it is necessary to involve local communities in environmental governance (Brondizio & Le Tourneau, 2016; Dudley et al., 2014).
Despite differences found in the decrease in the number of total illegal activities and the increase in illegal fishing activities in coastal/marine when compared with terrestrial PAs, we did not find significant differences for illegal activities of hunting and vegetation degradation. Overall, a greater number of fisheries-related offenses are expected in coastal marine areas. However, coastal marine PAs that occur in the Brazilian Amazon have also significant portions of forests (mainly mangrove formations). Thus, it is not surprising that illegal hunting and vegetation degradation were present in these areas in similar levels of terrestrial PAs. On the other hand, the differences presented here indicate the need for a more detailed evaluation of these different locations of PAs, which could be coupled with differences in strategies and conservation actions to be applied to individual areas (Barber et al., 2012; Margules & Pressey, 2000).
PAs are fundamental for biodiversity conservation across the Brazilian Amazon, and their establishment and maintenance is a key strategy for protection from the pressures and threats posed by human presence in tropical forests. Nonetheless, PAs are one of the most crucial factors contributing to reductions in deforestation in this biome. We report several threats that may impair long-term conservation and many efforts are still needed to address these issues. The use of enforcement reports generated by official government authorities provides us with a more nuanced view of the illegal activities taking place within PAs in the Brazilian Amazon. We demonstrated that this type of information can be useful as a complement to more sophisticated remote sensing techniques that usually fail to identify threats under the forest canopy. We have showed that the monitoring information helps to identify more problematic PAs in relation to the illegal use of natural resources and in relation to detailed categories of infraction. This can help managers to plan and implement specific conservation actions to individual areas in order to reduce illegal activities. Additionally, information regarding enforcement effort applied in each PA can be better quantified, which would help conservationists and practioners to be able to evaluate and set goals for different PAs under different regimes and locations. Implement management actions in and around PAs are key conservation issues that will need to be addressed to provide the realization of effectiveness goals of de facto preservation of the Brazilian Amazon.
Accessibility of the Brazilian Amazon federal protected areas
Accessibility of PAs defined as the intersection between the total area of a PA with the area of a 10 km buffer adjacent to roads and rivers located within or outside PAs. (A) rivers and shoreline accessibility; (B) roads accessibility; and (C) overall and PAs accessibility.
Population density of the Brazilian Amazon
Population density map of the Amazon biome elaborated from the “Brazilian statistical grid” for visualization purposes.
Amazon federal protected areas evaluated and explanatory variables
Amazon federal PAs evaluated (n = 118), Brazilian classification, IUCN classification, age in 2015, total area (km2), total number of illegal activities recorded (2010–2015), population density in a 50 km buffer from the perimeter of each PA and accessibility of a protected area (accessibility km2/total area km2). APA, Environmental Protected Area; ARIE, Area of Relevant Ecological Interest; ESEC, Ecological Reserve; PARNA, National Park; REBIO, Biological Reserve; FLONA, National Forest; RDS, Sustainable Development Reserve; RESEX, Extractive Reserve.
Categories and types of illegal activities
Categorization of illegal activities considering the infraction framework, the number of occurrences of each type of infraction (according to Brazilian Federal Decree 6514 (2008)), and the main characteristics of illegal activities.
Mann-Whitney U test results between the number of illegal activities in terrestrial and coastal/marine Brazilian Amazon federal PAs
Comparison between the number of illegal activities in the Brazilian Amazon federal PAs, and the PA location (coastal/marine, n = 13; or terrestrial, n = 105). The test was run separately for all illegal activities, hunting activities, illegal fishing, and flora degradation.