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Barboza, R. D., S. F. Lopes, W. M. S. Souto, H. Fernandes-Ferreira, and R. R. N. Alves. 2016. The role of game mammals as bushmeat In the Caatinga, northeast Brazil. Ecology and Society 21(2):2.
http://dx.doi.org/10.5751/ES-08358-210202
Research, part of a special feature on Why does hunting in tropical regions matter?

The role of game mammals as bushmeat In the Caatinga, northeast Brazil

1Departamento de Sistemática e Ecologia, Universidade Federal da Paraíba, Brazil, 2Departamento de Biologia, Universidade Estadual da Paraíba, Brazil, 3Universidade Federal do Piauí, Campus Amílcar Ferreira Sobral, Laboratório de Etnobiologia e Conservação (LECON), Piauí, Brazil, 4Universidade Federal Rural de Pernambuco, Departamento de Biologia, Programa de Pós-graduação em Ecologia, Recife, Pernambuco, Brazil

ABSTRACT

Although the use of wild mammals as a source of food has been better studied in tropical forest environments, their importance as a source of protein for human communities in semiarid environments is little known. In the latter, the availability of wild animal meat is limited in comparison to other environments. In the semiarid regions of northeastern Brazil, hunting wild mammals for their meat is traditional, playing a crucial role in the livelihoods and food security of various rural and urban communities, especially during the annual drought seasons. In this study, we investigated the role of wild mammals as bushmeat in 10 communities within the Caatinga biome in northeast Brazil. We used key-informant interviews, household surveys, and questionnaires to determine the species hunted and consumed. We found that about 30 species were used for bushmeat, with communities clustering into two main groups. We showed that in almost all municipalities visited, all mammals hunted were reported after interview days. A total of 46.9% of hunters consumed bushmeat at least once a week. However, preference for bushmeat over livestock was perceived to be more a matter of taste (61.50% of respondents) than a real need for protein supplementation from the wild. The ease of entering environmental areas where wild mammals can be found has disadvantages for wildlife in terms of pressure and overexploitation, especially where it concerns endangered species. The key to understanding the socioeconomic, cultural, and ecological contexts in which there are traditional uses is to develop conservationist strategies suitable for the socioeconomic reality of human populations.
Key words: conservation; ethnozoology; hunting practices; local ecological knowledge; mammals; semiarid region

INTRODUCTION

In tropical regions worldwide, the meat of wild animals (bushmeat) is part of the diets of rural communities and is also eaten in urban areas. In many cases, hunted animals can be an important income source for many rural people, and can form the basis of a highly lucrative trade (Elliott et al. 2002, Milner-Gulland and Bennett 2003, Wilkie et al. 2005, van Vliet et al. 2014, 2015). Although invertebrates can be locally important dietary items, it is the larger terrestrial vertebrates that make up most of the wild animals eaten by humans (Alves 2012). In particular, mammals contribute most of the biomass of the bushmeat consumed in terrestrial environments (Silvius et al. 2004, van Vliet et al. 2014, Mesquita and Barreto 2015).

In semiarid regions, such as the Brazilian Caatinga, wild mammal meat can be a vital source of animal protein for human communities there because the availability of fish or other sources is limited. In this ecoregion, wild meat can be especially critical during the early drought periods typical in this environment, when crops are scarce and domestic animals may die because of starvation and dehydration (Miranda and Alencar 2007, Alves et al. 2009, Pereira and Schiavetti 2010, Fernandes-Ferreira et al. 2012).

Although mammalian diversity in semiarid environments is lower than in tropical rainforests, the hunting of mammals is still important in supplying meat and other products (Albuquerque et al. 2012). Hunting in the Caatinga region has long been traditionally practiced for subsistence purposes (Alves et al. 2009, 2012, Albuquerque et al. 2012). However, some authors suggest that currently, wildlife hunting is less of a subsistence activity, but one linked to recreation and entertainment (Alves et al. 2009, 2012). Whatever the reasons for hunting may be, overexploitation of wildlife in the Caatinga is a real threat to the ecoregion’s biodiversity (Leal et al. 2005a, Alves et al. 2009, Fernandes-Ferreira et al. 2012); numerous species, particularly mammals, are threatened with extinction (Alves et al. 2009, 2012). In this scenario, the importance of ethnozoological studies is clearly evident (Alves and Souto 2015).

In this study, we investigated the importance of mammals as bushmeat in a number of localities within the Caatinga biome, northeast Brazil. We interviewed active hunters within a total of 10 municipalities in 4 different states in northeast Brazil, aiming to estimate the number of species of mammals that are used as a food resource in the region and to investigate if there is a change in the taxonomic richness of mammalian game species according to geographic location.

METHODS

Study area

All study localities were situated within the Brazilian semiarid region in the northeast of the country. This region (around 750,000 km²) is mostly occupied by the Caatinga biome, an ecoregion predominantly comprising xerophytic, woody, thorny, and deciduous vegetation (Sampaio 1995, Costa et al. 2007). The region is characterized by a warm, dry climate (Veloso et al. 1991), experiencing drought periods that can last up to 11 months in a year (Ab’Saber 1977). These unique climatic conditions have led to the emergence of specific morphological and physiological adaptations in the fauna and flora of the biome (Rodrigues 1996, Vieira et al. 2009, Albuquerque et al. 2012).

The Caatinga contains a relatively low animal species diversity and only a small number of endemics (Andrade-Lima 1982, Prance 1987, Vanzolini 1996). However, the region is considered to harbor a unique component of Brazil’s biodiversity (Leal et al. 2005a). A total of 153 mammal species are found in the Caatinga, more than those found in the Pantanal swamps (n = 113) or the Grande Chaco (n = 102; Meserve 2007), though less than in the Amazon Rainforest (n = 350; Meserve 2007), Atlantic Forest (n = 261; Myers et al. 2000), and Cerrado (n = 199; Klink and Machado 2005). Despite advances in our knowledge of the mammals of the Caatinga, many areas of the Caatinga have not yet been studied, so undescribed species are likely to be present (Albuquerque et al. 2012).

Study localities

Data were collected from 10 municipalities within 4 different states in the northeast region of Brazil: Caicó (CC), Jardim de Piranhas (JP), and São Fernando (SF) in Rio Grande do Norte (RN); Buriti (B), Milagres do Maranhão (MM), and São Benedito do Rio Preto (SBP) in Maranhão (MA); José Freitas (JF), União (U), and Lagoa Alegre (LA) in Piauí (PI); and the municipality of Sumé (S) in Paraíba (PB; Fig. 1)

Before starting data collection, we introduced ourselves, explained the nature and objectives of our research, and asked the respondents for permission to record their answers to our questions. Approval for the study was obtained from the Ethics Committee of Universidade Federal da Paraiba (UFPB).

We selected study sites on the basis of the following criteria: (1) evidence of intense hunting activities; (2) accessibility; (3) lack of studies on ethnoecology and ethnozoology in those regions; and (4) cultural diversity. We selected the informants in this sample utilizing the “snowball” technique (Posey 1986). In all cases, species mentioned as hunted by the respondents were identified directly from observation of animals killed and donated to the project, photographs taken during the interviews of animals hunted, and on the basis of their vernacular names (with the aid of taxonomists familiar with the fauna of the study area).

Procedures

Field research was conducted by the first author of the manuscript between April 2010 and October 2012. We interviewed a total of 413 hunters in rural and urban areas (399 men and 14 women), 40 individuals in each city visited except Jardim de Piranhas, RN (n = 42) and Sumé, PB (n = 51).

Semistructured interviews, complemented by free interviews, were conducted with respondents in each of the localities surveyed (Huntington 2000). The aim of these interviews was to collect quantitative estimates of hunting practices and mammal bushmeat sources used by the different communities. Among the interviewees, we selected key informants (more experienced hunters) or “native specialists,” i.e., people who considered themselves and were considered by the community as very knowledgeable about the culture in this area (Hays 1983, Marques 2002). The interview contained questions on the hunters’ demographics (Table 1), main livelihood activities, and income, as well as information on protein sources consumed, mammals hunted, access to mammalian bushmeat, and preferences.

To analyze whether the species richness cited by informants was the same estimated richness for the 10 surveyed areas, we utilized the rarefaction technique with the standardization of sampling effort by the number of citations recorded (Gotelli and Colwell 2001, Magurran 2011). For this, we compared, using 1000 randomizations, the species richness observed using the Sobs Mao Tau with the species richness estimated using Jackknife 1, which was the estimator that correlated most closely with observed richness (Walther and Moore 2005). The accumulation curves were calculated using the software EstimateS© version 8.2 (Colwell 2009). Species mentioned at each city surveyed were compared using the Jaccard similarity coefficient (presence/absence data). Cluster analyses were performed using the software PRIMER-E (Clarke and Gorley 2006) with the unweighted pair group method using arithmetic averages (UPGMA). Graphs were prepared using the program STATISTICA (Statsoft 2001).

RESULTS

A total of 38 species of wild mammals were reported as hunted by the interviewees. Of these, 30 species were bushmeat by hunters and other people in the areas surveyed. The order with the highest number of recorded species was Carnivora (15 species), followed by Rodentia (9), Primates (3), Artiodactyla (2), Pilosa (2), Cingulata (2), Didelphimorphia (2), Lagomorpha (1), and Chiroptera (1; Table 2). Among the mammals used as bushmeat, the most cited (more than 160 times) were: red brocket deer Mazama americana (n = 167); grey brocket deer M. gouazoubira (n = 173); tree ocelot Leopardus wiedii (n = 183); Spix’s yellow-toothed cavy Galea spixii (n = 192); Southern tamandua Tamandua tetradactyla (n = 246); Brazilian guinea pig Cavia aperea (n = 324); rock cavy Kerodon rupestris (n = 335); six-banded armadillo Euphractus sexcinctus (n = 369); and nine-banded armadillo Dasypus novemcinctus (n = 395).

Although a number of species were reported as being used as bushmeat in all locations, there were variations in richness by location. In the municipalities of Rio Grande do Norte State, hunters indicated the use of at least 19 species, and in the states of Piauí and Maranhão, 30 species were mentioned. The place where there was a smaller number of species used as bushmeat was Sumé, PB, with 15 species reported by hunters.

The richness estimator indicated that in almost all municipalities visited, 100% of mammal species of hunting value were sampled for each location, except the municipality of Jardim de Piranhas, where the sampling effort was 87%. However, in all cases, a clear stabilization of the asymptote was demonstrated in the species accumulation curve (Fig. 2). Observed species richness (n = 30) was similar (n = 30) to the estimated number, which reflected the universe of mammal species used as bushmeat consumed by cited interviews.

Considering the game mammals’ richness of each location visited, the similarity dendrogram showed the formation of two well-defined major groups with 65% similarity to each other and subsequently the formation of similar subgroups (Fig. 3). The first group comprised the species cited in three municipalities in RN plus the city located in Paraíba, which are geographically close. The second group formed the species mentioned in MA and PI, showing 95% similarity.

Hunting pressure was constant throughout the year and hunters employed various techniques adapted to specific habitats and mammalian species. The most common included weapons, hunting dogs, and different kinds of traps. At least 68% of respondents described that open forest of Caatinga was preferred for hunting because visibility was higher than in habitats that had very dense vegetation, where walking off the trails was challenging. Because the Caatinga biome represents a mosaic of phytophysiognomic formations, hunters stated that degraded areas supplied approximately 30% of the animals killed and little diversity of small mammal species at short distances from their municipalities (< 4 km), whereas undisturbed or slightly disturbed areas supplied the greatest diversity of mammalian species including those of major commercial interest, e.g., grey brocket deer, red brocket deer, and armadillos, which were preferable sources of meat for local traditional festivities. To reach undisturbed areas of the semiarid region, the majority of hunters (74%) described the benefits of using motorized vehicles to cover distances > 50 km from their homes. This practice decreased the time and effort to cover long distances and increased the chances of having good catches in those areas. According to 66% of respondents, over the past 15 years, the continued use of motorcycles, dogs, and sophisticated shotguns has led to at least 35% decrease in the abundance of game animals in surveyed area.

Regarding the frequency that hunters consumed the meat of wild mammals, a total of 194 (46.97%) respondents answered at least once a week, 27.84% (n = 115) stated every 15 days, 15.98 % (n = 66) stated at least every 1 - 2 weeks and 9.20% (n = 38) consumed wild meat every three months or more during the year. According to the hunters, when they killed more than one specimen and the product of the hunt was intended for personal consumption, the meat was usually shared with relatives or even friends. In the opinion of 62.7% (n = 259) of the respondents, the more sociable and supportive the hunter was, the more consideration and respect he got within the family and among other beneficiaries of the hunt.

When asked about the reasons for preference of wild meat over meat of domestic animals, the majority of respondents (n = 254, 61.50%) said that the preference for bushmeat today was a matter of taste than for a real need for protein supplementation. Even with some reservations due to cultural issues of food taboos for some wild species, such as armadillos, it was noticed that the majority of respondents (n = 388, 94%) considered all wild meat as noble, clean, and healthy. Although appreciated as local delicacies, six-banded armadillo meat is considered an allergenic food, and it is not advised to be eaten by individuals with health problems such as infections, wounds, venereal diseases, and hepatitis, or during menstruation or pregnancy. This taboo may be linked to the omnivorous and scavenger dietary habits of this species. According to 188 (45.52%) respondents who were farmers and ranchers, the meat of wild mammals is better when compared to farm animals such as cattle, goats, and pigs.

According to the majority of respondents (n = 262, 63.4%), high preference for meat of wild mammal species also extended to individuals who did not hunt, but purchased the meat of these animals. Of the species cited, the majority of respondents (n = 304, 73.6%) highlighted the distinctive flavor of their meat, especially when prepared with the addition of alcoholic beverages, herbs, fruits, and other spices. The meat could be eaten either grilled, in a soup, fried, baked, or smoked in a handcrafted way.

For all wild mammal species used as food, there is some level of concern regarding conservation. Of these, in addition to being included in the International Union Red List species for Conservation of Nature (IUCN Red List), seven were listed in the Appendices of Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES 2015) and six species were listed on the Brazilian Red List of threatened fauna (MMA 2014). The species found on the IUCN Red List were in different categories: 24 in “low concern” (LC), 1 in “data deficient” (DD), 1 in “vulnerable” (VU; Leopardus tigrinus), and 3 in “nearly threatened” (NT; Speothos venaticus, Leopardus wiedii, and Panthera onca). As for the species in the Brazilian Red List, five were classified as vulnerable, especially the group of carnivores, and one species was considered endangered (EN; Leopardus tigrinus).

DISCUSSION

Our results showed that the consumption of wild mammal meat was the main reason for hunting these animals in the Brazilian semiarid region, because of the 38 species of mammals hunted in the region, 29 (76%) were consumed as a source of protein. This trend has been observed in other studies conducted in the Brazilian semiarid land (Alves et al. 2009, 2012, Pereira and Schiavetti 2010, Barbosa et al. 2011, Melo et al. 2014), but also in other biomes (Bodmer et al. 1997, Lopes and Ferrari 2000, Hanazaki et al. 2009, Dantas-Aguiar et al. 2011, Souza and Alves 2014, Mesquita and Barreto 2015), in which mammals represented the preferred group used as a source of game meat. Still, as shown by other authors, there are other uses of vertebrates in the Caatinga, related to hunting for bushmeat, because by-products of animals slaughtered for bushmeat such as horns, hides, skulls, and others, are used for other purposes, maximizing the use of local resources (Alves et al. 2012). Other uses of game mammals in the northeastern semiarid region include the breeding of pets, and even the use of their products in folk medicine handicrafts and mystical/religious practices (Alves 2009, Alves et al. 2009, Souto et al. 2011).

Our results confirmed that in the Brazilian semiarid region, wild mammals represented a major source of bushmeat, reflecting a situation that occurs in all Brazilian biomes (Becker 1981, Hanazaki et al. 2009, van Vliet et al. 2014, Mesquita and Barreto 2015). The exploitation of a high proportion (24%) of mammalian species that occur in the Caatinga reinforces the hunting importance of this taxon. Our data suggest that, despite having a lower species richness than in other Brazilian biomes, in the Caatinga, game richness is equal to or greater proportionally. This may be because in this region hunted species are of different sizes, because the larger species are scarce. In other Brazilian biomes, hunting for consumption usually targets large species, particularly in areas of the Atlantic Forest (Cullen et al. 2000, Hanazaki et al. 2009, Souza and Alves 2014) and the Amazon Rainforest (Pezzuti and Chaves 2009, Rosas-Ribeiro et al. 2012).

It was also evident that there were a number of mammalian species (n = 15) that were exploited in all localities surveyed, indicating the spread of the same uses as protein resource for local communities and geographical continuity in the selection of exploited resources of mammalian fauna in the Brazilian semiarid region. Nevertheless, there was the case of species mentioned in only some states, which resulted in the formation of different groups and subgroups according to the locality studied, as revealed by the similarity analysis. This suggests that variations in the composition of species of mammals in the ecoregions of the Caatinga influences the choice of species hunted. The municipalities studied in the states of Maranhão and Piauí, for example, showed areas of environmental transition between Caatinga and Cerrado, enabling ecological communities of these two biomes to be in contact, increasing the diversity of species in the region, and thus increasing their availability to hunters. This was reflected in the richness of species cited by respondents in these areas and contributed to the greater similarity between them.

Some of the game mammals cited by the respondents, such as Speothos venaticus, Panthera onca, Puma concolor, Eira barbara, Lontra longicaudis, Nasua nasua, Didelphis marsupialis, Hydrochoerus hydrochaeris, Cuniculus paca, and Coendou prehensilis, exhibit very different distributions in Brazil (Chiarello et al. 2008, Canale et al. 2012, Carvalho and Gonçalves 2013, Rodrigues et al. 2013). However, in some areas of the Caatinga displaying drier shrubland, such as in the states of Rio Grande do Norte and Paraíba, the records of these species are scarce or very old or these species are considered extinct (Keuroghlian et al. 2012), whereas in more dense, humid areas of the Caatinga, such as in Maranhão and Piauí, these species find refuge areas with different vegetation types of the Caatinga (Bucher 1982, Veloso et al. 1991, Castelletti et al. 2003). Our results reflected this situation because these species were most cited in the locations of Maranhão and Piauí.

These results demonstrated the close relationship that local hunters have with the natural environment in which they live, exploiting the resources available in the region. The use of local and easily accessible resources is certainly related to historical and cultural aspects, that is, hunting tradition focusing on local species, reflecting the transfer of knowledge from generation to generation. Our results are in agreement with other ethnobotanical and ethnozoological studies that demonstrate that the diversity of animals and plants known and used by human populations can be influenced by the diversity found in the environment (Bennett 1992, Phillips and Gentry 1993, Robinson and Bennett 2004, Alves and Rosa 2006, 2007, 2010). These studies suggest that more easily found animals and plants are more likely to be used by local people, thus increasing the likelihood of these resources to be incorporated into the local culture.

Differences in hunting activities in different habitat types of Caatinga are explained by hunters’ cultural preferences. Our results suggest that there is potential to increase hunting in open areas and during dry seasons, although dense vegetation with little anthropogenic disturbance is preferable for hunting specific mammals. Studies have demonstrated that peri-urban hunters commonly recognize different types of habitats for several purposes, and despite hunters’ preferences for mature forest, disturbed forest has higher hunting pressure due to proximity of communities and villages, whereas mature and dense forest are more distant (Fa et al. 2002, van Vliet and Nasi 2008, Mesquita and Barreto 2015). Moreover, in the Brazilian semiarid region as well as in several regions of the world, the use of motorized vehicles has been practiced not only by hunters but also by specialized middlemen in the illegal trade of bushmeat, so this contributes to overexploitation of many game species besides deforestation of the remaining vegetation of biomes (Juste et al. 1995, Fa et al. 2006, Di Bitetti et al. 2008, Read et al. 2010, Mockrin et al. 2011). The hunting impacts on wildlife are a complex phenomenon that varies in space and over time, and little is known on the subject (Grignolio et al. 2011). For decades, many target species of hunters have been frugivorous or granivorous, which are important in seed dispersion (Wright et al. 2007). We emphasize that a higher level of accessibility to preserved areas and the use of new technologies has led to a change in the current hunting scenario in the Brazilian Northeast.

It was noticed that the frequency of meat consumption of wild mammals by hunters did not follow a specific pattern, but most ate game meat on a regular basis, every week or every fortnight. Although there is little information about the frequency of the consumption of game meat in northeast Brazil, it is believed that until a few decades ago, many local residents consumed bushmeat almost daily during dry periods, when livestock herds died of thirst and hunger (Leal et al. 2005b, Alves et al. 2009). Today, despite the fact that droughts are frequent and continue to decimate herds, improvements in social conditions in the Brazilian semiarid region enables the purchase of domestic animal meat, also at lower prices compared to game meat.

In the areas surveyed, consumption of game mammals is associated with social interactions among hunters, including the sharing of game meat. Similar situations have been reported in other regions of Brazil and the world. Fa et al. (2003) documented the exploitation of wild meat in the world’s tropical forests, noting that the sharing of meat between urban hunters was quite common as a means of socializing. Cullen et al. (2004) observed the effects of hunting in tropical forest fragments in Brazil and found regular social interactions among local hunters. In a study of hunting in a rural settlement in the Mato Grosso Amazon, Brazil, Trinca and Ferrari (2006) found that it is quite common among local hunters to slaughter killed game animals and share the meat, especially for mammals.

Our results show that the preference of wild mammal meat was highlighted as an important incentive for the demand of this product in the areas visited, where it was regarded by hunters as a resource that has flavor, aroma, and distinct nutritional value in relation to other sources of animal protein. Previous studies corroborate this finding. Mbete et al. (2011), for example, pointed out that the taste category and cultural aspects are the most important things that rouse consumption of the main species of cloven-hoof animals, rodents, and primates in the homes of Brazzaville (Congo). Lindsey et al. (2012) reported that in certain urban areas, the preference depending on the taste of meat can be as high as 100% among consumers, encouraging hunters to provide increasing amounts of bushmeat.

Essentially none of the respondents showed any concern for the conservation of mammals hunted in the places visited. This situation is worrisome, because the potential impact that hunting for meat has on wildlife is known (Milner-Gulland and Bennett 2003, Albrechtsen et al. 2007, Care for the Wild International 2007, Esser et al. 2012). According to the IUCN (2008), almost a quarter (22%) of mammalian species in the world are endangered species and 836 (15%) are classified as data deficient (Schipper et al. 2008, Vié et al. 2009), where hunting exerts substantial pressure on mammals.

Although most of the species mentioned in this research are categorized in the Red List as “least concern,” it should be considered that at the local level these populations may suffer overexploitation and extinction. In the Caatinga, there are historical accounts of extinctions and eliminations of fauna by excessive hunting. For example, hunting activities for subsistence purposes has almost eradicated the three-banded armadillo Tolypeutes tricinctus (Linnaeus, 1758) in the Brazilian semiarid region (IBAMA 2004, Miranda et al. 2014) and the Brazilian tapir Tapirus terrestris (Linnaeus, 1758), which is currently considered regionally extinct and possibly nonexistent in this biome since the 1980s (Medici et al. 2012). In addition, the rapid deforestation of the Caatinga biome, increasing urbanization, incorporation of new technologies in hunting activities, and, above all, the continued intensification of illegal exploitation of bushmeat has led to instabilities in the population structure of game animals. This scenario is in concordance with other studies (Milner-Gulland and Bennett 2003, Parliamentary Office of Science and Technology 2005, Bennett et al. 2007, Endo et al. 2010).

Some studies suggest that important game mammals recorded in Caatinga areas, including the brocket deer and red deer, the armadillos such as the nine-banded armadillo (the game species most appreciated by local hunters) and six-banded armadillo, are found in relictual populations in the Brazilian semiarid lands because of hunting pressure that they suffered over the last centuries (Oliveira et al. 2003, Medri et al. 2011, Desbiez et al. 2012). Similarly, Tamandua tetradactyla is considered by the hunters of the locations surveyed as a species that is increasingly hard to find, even on hunting trips with the help of dogs. This was corroborated by Smith (2007), who states that their slow speed and ease of being spotted because of their color and size make for easy capture. Therefore, we can infer that the hunting pressure on these animals is increasing greatly in the Brazilian semiarid area because of the demand for the meat of such animals as well as the use of multiple hunting strategies, with emphasis on the use of firearms and hunting dogs along with motorized transport to the hunting grounds.

Our results indicate that a significant proportion of the mammals that occur in the Caatinga have been exploited as a protein source in the areas surveyed, which is the main reason for hunting in the area. However, it is noteworthy that the killing of wild game during hunting activities is not fully associated with a need for subsistence because hunting is also motivated by recreation, entertainment, trade, or trafficking. In addition, our data indicated that the number of game mammals recorded in this study corresponded to almost all mammals exploited as meat sources in the Brazilian semiarid region and that exploitation was directly associated with species richness in each area, suggesting a greater prevalence of consumption of species endemic to the specified region.

This scenario, associated with several factors that have had an impact on the Caatinga, has caused a population decline of many local species of mammals, and even their extinction, in most of this biome. This situation shows that subsistence hunting in the Brazilian semiarid region, as elsewhere, is influenced by a complex set of biological, socioeconomic, political, and institutional factors that are essential to understand this multidimensional framework for the design of effective conservation solutions. Therefore, the combination of more rigorous supervision by conservation agencies through medium- and long-term campaigns in environmental education and population awareness are immediate strategies to reduce the demand for wildlife.

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ACKNOWLEDGMENTS

We thank to CNPq/Edital Universal program (476460/2012-3 and 458312/2014-2) for financial support. The last author acknowledges CNPq for awarding Productivity in Research scholarship. Special thanks are due to all interviewees, who kindly shared their knowledge with us.

LITERATURE CITED

Ab’Saber, A. N. 1977. Espaços ocupados pela expansão dos climas secos na América do Sul, por ocasião dos períodos glaciais quaternários. Paleoclimas 3:1-19.

Albrechtsen, L., D. W. Macdonald, P. J. Johnson, R. Castelo, and J. E. Fa. 2007. Faunal loss from bushmeat hunting: empirical evidence and policy implications in Bioko Island. Environmental Science & Policy 10(7-8):654-667. http://dx.doi.org/10.1016/j.envsci.2007.04.007

Albuquerque, U. P., E. L. Araújo, A. C. A. El-Deir, A. L. A. Lima, A. Souto, B. M. Bezerra, E. M. N. Ferraz, E. M. X. Freire, E. V. S. B. Sampaio, F. M. G. Las-Casas, G. J. B. Moura, G. A. Pereira, J. G. Melo, M. A. Ramos, M. J. N. Rodal, N. Schiel, R. M. Lyra-Neves, R. R. N. Alves, S. M. Azevedo-Júnior, W. R. Telino-Júnior, and W. Severi. 2012. Caatinga revisited: ecology and conservation of an important seasonal dry forest. Scientific World Journal 2012(2012):1-18. http://dx.doi.org/10.1100/2012/205182

Alves, R. R. N. 2009. Fauna used in popular medicine in Northeast Brazil. Journal of Ethnobiology and Ethnomedicine 5(1):1-30. http://dx.doi.org/10.1186/1746-4269-5-1

Alves, R. R. N. 2012. Relationships between fauna and people and the role of ethnozoology in animal conservation. Ethnobiology and Conservation 1:1-69.

Alves, R. R. N., M. B. R. Gonçalves, and W. L. S. Vieira. 2012. Caça, uso e conservação de vertebrados no semiárido Brasileiro. Tropical Conservation Science 5(3):394-416.

Alves, R. R. N., L. E. T. Mendonça, M. V. A. Confessor, W. L. S. Vieira, and L. C. S. Lopez. 2009. Hunting strategies used in the semi-arid region of northeastern Brazil. Journal of Ethnobiology and Ethnomedicine 5(12):1-50. http://dx.doi.org/10.1186/1746-4269-5-12

Alves, R. R. N., and I. L. Rosa. 2006. From cnidarians to mammals: the use of animals as remedies in fishing communities in NE Brazil. Journal of Ethnopharmacology 107(2):259-276. http://dx.doi.org/10.1016/j.jep.2006.03.007

Alves, R. R. N., and I. L. Rosa. 2007. Biodiversity, traditional medicine and public health: where do they meet? Journal of Ethnobiology and Ethnomedicine 3:1-14. http://dx.doi.org/10.1186/1746-4269-3-14

Alves, R. R. N., and I. L. Rosa. 2010. Trade of animals used in Brazilian traditional medicine: trends and implications for conservation. Human Ecology 38(5):691-704. http://dx.doi.org/10.1007/s10745-010-9352-0

Alves, R. R. N., and W. M. S. Souto. 2015. Ethnozoology: a brief introduction. Ethnobiology and Conservation 4(1):1-13. http://dx.doi.org/10.15451/ec2015-1-4.1-1-13

Andrade-Lima, D. 1982. Present-day forest refuges in northeastern Brazil. Pages 245-251 in G. T. Prance, editor. Biological diversification in the tropics. Columbia University Press, New York, New York, USA.

Barbosa, J. A. A., V. A. Nobrega, and R. R. N. Alves. 2011. Hunting practices in the semiarid region of Brazil. Indian Journal of Traditional Knowledge 10(3):486-490.

Becker, M. 1981. Aspectos da caça em algumas regiões do cerrado de Mato Grosso. Brasil Florestal 11(47):51-63.

Bennett, J. 1992. A glut of gibbons in Sarawak — is rehabilitation the answer? Oryx 26(3):157-164. http://dx.doi.org/10.1017/S0030605300023590

Bennett, E. L., E. Blencowe, K. Brandon, D. Brown, R. W. Burn, G. Cowlishaw, G. Davies, H. Dublin, J. E. Fa, E. J. Milner-Gulland, J. G. Robinson, J. M. Rowcliffe, F. M. Underwood, and D. S. Wilkie. 2007. Hunting for consensus: reconciling bushmeat harvest, conservation, and development policy in West and Central Africa. Conservation Biology 21(3):884-887. http://dx.doi.org/10.1111/j.1523-1739.2006.00595.x

Bodmer, R. E., J. F. Eisenberg, and K. H. Redford. 1997. Hunting and the likelihood of extinction of Amazonian mammals. Conservation Biology 11(2):460-466. http://dx.doi.org/10.1046/j.1523-1739.1997.96022.x

Bucher, E. H. 1982. Chaco and Caatinga-South American arid savannas, woodlands and thickets. Pages 48-79 in B. J. Huntey and B. H. Walther, editors. Ecology of tropical savannas. Springer-Verlag, Berlin, Germany. http://dx.doi.org/10.1007/978-3-642-68786-0_4

Canale, G. R., C. A. Peres, C. E. Guidorizzi, C. A. F. Gatto, and M. C. M. Kierulff. 2012. Pervasive defaunation of forest remnants in a tropical biodiversity hotspot. PloS ONE 7(8):e41671. http://dx.doi.org/10.1371/journal.pone.0041671

Care for the Wild International. 2007. Going to pot: the neotropical bushmeat crisis and its impact on primate populations. First edition. Care for the Wild International, Kingsfold, UK and and Pro Wildlife, Munich, Germany.

Carvalho Jr, E. A. R., and R. Gonçalves. 2013. Factors affecting big cat hunting in Brazilian protected areas. Tropical Conservation Science 6(2):303-310.

Castelletti, C. H. M., A. M. M. Santos, M. Tabarelli, and J. M. C. Silva. 2003. Quanto ainda resta da Caatinga? Uma estimativa preliminar. Pages 91-100 in I. R. Leal, M. Tabarelli, and J. M. C. Silva, editors. Ecologia e Conservação da Caatinga. Universidade da UFPE, Recife, Brasil.

Chiarello, A. G., L. M. S. Aguiar, R. Cerqueira, F. R. Melo, F. H. G. Rodrigues, and V. M. Silva. 2008. Mamíferos Ameaçados de Extinção no Brasil. Pages 681-702 in A. B. M. Machado, G. M. Drummond, and A. P. Paglia, editors. Livro Vermelho da Fauna Brasileira Ameaçada de Extinção. Ministério do Meio Ambiente/Fundação Biodiversitas, Brasília and Belo Horizonte, Brazil.

Clarke, K. R., and R. N. Gorley. 2006. PRIMER v6: User Manual/ Tutorial. PRIMER-E, Plymouth, UK.

Colwell, R. 2009. EstimateS: statistical estimation of species richness and shared species from samples v8: User’s guide and application. [online] URL: http://viceroy.eeb.uconn.edu/estimates/EstimateSPages/EstSUsersGuide/EstimateSUsersGuide.htm

Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES). 2015. Checklist of CITES species. CITES, Geneva, Switzerland. [online] URL: http://checklist.cites.org/#/en

Costa, R. C., F. Soares Araújo, and L. W. Lima-Verde. 2007. Flora and life-form spectrum in an area of deciduous thorn woodland (caatinga) in northeastern, Brazil. Journal of Arid Environments 68(2):237-247. http://dx.doi.org/10.1016/j.jaridenv.2006.06.003

Cullen Jr, L., R. E. Bodmer, and C. V. Pádua. 2000. Effects of hunting in habitat fragments of the Atlantic forests, Brazil. Biological Conservation 95(1):49-56. http://dx.doi.org/10.1016/s0006-3207(00)00011-2

Cullen Jr, L., R. E. Bodmer, C. V. Padua, and J. D. Ballou. 2004. Mammalian densities and species extinctions in Atlantic Forest fragments: the need for population management. Pages 211–226 in K. M. Silvius, R. E. Bodmer, and J. M. V. Fragoso, editors. People in nature: wildlife conservation in South and Central America. Columbia University Press, New York, New York, USA.

Dantas-Aguiar, P. R., R. M. Barreto, D. Santos-Fita, and E. B. Santos. 2011. Hunting activities and wild fauna use: a profile of Queixo D'antas Community, Campo Formoso, Bahia, Brazil. Bioremediation, Biodiversity and Bioavailability 5(1):34-43.

Desbiez, A. L. J., A. Keuroghlian, B. de Mello Beisiegel, E. P. Medici, A. Gatti, A. R. M. Pontes, C. B. Campos, C. F. Tófoli, E. A. M. Júnior, and F. C. Azevedo. 2012. Avaliação do risco de extinção do cateto Pecari tajacu Linnaeus, 1758, no Brasil. Biodiversidade Brasileira 1:74-83.

Di Bitetti, M. S., A. Paviolo, C. A. Ferrari, C. De Angelo, and Y. Di Blanco. 2008. Differential responses to hunting in two sympatric species of brocket deer (Mazama americana and M. nana). Biotropica 40(5):636-645. http://dx.doi.org/10.1111/j.1744-7429.2008.00413.x

Elliott, J., R. Grahn, G. Sriskanthan, and C. Arnold. 2002. Wildlife and poverty study. Livestock and Wildlife Advisory Group, London, UK.

Endo, W., C. A. Peres, E. Salas, S. Mori, J.-L. Sanchez-Vega, G. H. Shepard, V. Pacheco, and D. W. Yu. 2010. Game vertebrate densities in hunted and nonhunted forest sites in Manu National Park, Peru. Biotropica 42(2):251-261. http://dx.doi.org/10.1111/j.1744-7429.2009.00546.x

Esser, H. J., Y. Liefting, R. Kays, and P. A. Jansen. 2012. A record of striped hog-nosed skunk Conepatus semistriatus in central Panama, between two known sub-ranges. Small Carnivore Conservation 47:62-64.

Fa, J. E., D. Currie, and J. Meeuwig. 2003. Bushmeat and food security in the Congo Basin: linkages between wildlife and people’s future. Environmental Conservation 30(1):71-78. http://dx.doi.org/10.1017/s0376892903000067

Fa, J. E., C. A Peres, and J. Meeuwig. 2002. Bushmeat exploitation in tropical forests: an intercontinental comparison. Conservation Biology 16(1):232-237. http://dx.doi.org/10.1046/j.1523-1739.2002.00275.x

Fa, J. E., S. Seymour, J. Dupain, R. Amin, L. Albrechtsen, and D. Macdonald. 2006. Getting to grips with the magnitude of exploitation: bushmeat in the Cross-Sanaga rivers region, Nigeria and Cameroon. Biological Conservation 129(4):497-510. http://dx.doi.org/10.1016/j.biocon.2005.11.031

Fernandes-Ferreira, H., S. V. Mendonça, C. Albano, F. S. Ferreira, and R. R. N. Alves. 2012. Hunting, use and conservation of birds in Northeast Brazil. Biodiversity and Conservation 21(1):221-244. http://dx.doi.org/10.1007/s10531-011-0179-9

Gotelli, N. J., and R. K. Colwell. 2001. Quantifying biodiversity: procedures and pitfalls in the measurement and comparison of species richness. Ecology Letters 4(4):379-391. http://dx.doi.org/10.1046/j.1461-0248.2001.00230.x

Grignolio, S., E. Merli, P. Bongi, S. Ciuti, and M. Apollonio. 2011. Effects of hunting with hounds on a non-target species living on the edge of a protected area. Biological Conservation 144(1):641-649. http://dx.doi.org/10.1016/j.biocon.2010.10.022

Hanazaki, N., R. R. N. Alves, and A. Begossi. 2009. Hunting and use of terrestrial fauna used by Caiçaras from the Atlantic Forest coast (Brazil). Journal of Ethnobiology and Ethnomedicine 5:1-36. http://dx.doi.org/10.1186/1746-4269-5-36

Hays, T. E. 1983. Ndumba folk biology and general principles of ethnobotanical classification and nomenclature. American Anthropologist 85:592-611. http://dx.doi.org/10.1525/aa.1983.85.3.02a00050

Huntington, H. P. 2000. Using traditional ecological knowledge in science: methods and applications. Ecological Applications 10(5):1270-1274. http://dx.doi.org/10.1890/1051-0761(2000)010[1270:utekis]2.0.co;2

Instituto Brasileiro do Meio Ambiente e dos Recursos Naturais Renováveis (IBAMA). 2004. Análise Integrada. Pages 1-136 in C. E. Brasil, editor. Estudo de Impacto Ambiental Projeto de Integração do Rio São Francisco com Bacias Hidrográficas do Nordeste Setentrional. IBAMA, Brasília, DF, Brasil.

International Union for the Conservation of Nature (IUCN). 2008. Mammals. IUCN Red List of Threatened Species, Cambridge, UK. [online] URL: http://www.iucnredlist.org/mammals

Juste, J., J. E. Fa, J. P. Del Val, and J. Castroviejo. 1995. Market dynamics of bushmeat species in Equatorial Guinea. Journal of Applied Ecology 32(3):454-467. http://dx.doi.org/10.2307/2404644

Keuroghlian, A., A. L. J. Desbiez, B. B. de Mello, E. P. Medici, A. Gatti, P. A. R. M., C. B. Campos, C. F. Tófoli, E. A. Moraes Júnior, F. C. Azevedo, G. M. Pinho, J. L. P. Cordeiro, T. S. Santos Junior, A. A. Morais, P. R. Mangini, K. Flesher, L. F. Rodrigues, and L. B. Almeida. 2012. Avaliação do risco de extinção do queixada Tayassu pecari Link, 1795, no Brasil. Biodiversidade Brasileira 1(3):84-102.

Klink, C. A., and R. B. Machado. 2005. Conservation of the Brazilian cerrado. Conservation Biology 19(3):707-713. http://dx.doi.org/10.1111/j.1523-1739.2005.00702.x

Leal, I. R., J. M. C. Da Silva, M. Tabarelli, and T. E. Lacher Jr. 2005a. Mudando o curso da conservação da biodiversidade na Caatinga do Nordeste do Brasil. Megadiversidade 1(1):139-146.

Leal, I. R., J. M. C. Da Silva, M. Tabarelli, and T. E. Lacher Jr. 2005b. Changing the course of biodiversity conservation in the Caatinga of northeastern Brazil. Conservation Biology 19(3):701-706. http://dx.doi.org/10.1111/j.1523-1739.2005.00703.x

Lindsey, P., G. Balme, M. Becker, C. Begg, C. Bento, C. Bocchino, A. Dickman, R. Diggle, H. Eves, P. Henschel, D. Lewis, K. Marnewick, J. Mattheus, J. W. Mcnutt, R. McRobb, N. Midlane, J. Milanzi, R. Morley, M. Murphree, P. Nyoni, V. Opyene, J. Phadima, N. Purchase, D. Rentsch, C. Roche, J. Shaw, H. van der Westhuizen, N. van Vliet, and P. Zisadza. 2012. Illegal hunting and the bush-meat trade in Savanna Africa: drivers, impacts and solutions to address the problem. Panthera/Zoological Society of London/Wildlife Conservation Society, New York, New York, USA.

Lopes, M. A., and S. F. Ferrari. 2000. Effects of human colonization on the abundance and diversity of mammals in eastern Brazilian Amazonia. Conservation Biology 14(6):1658-1665.

Magurran, A. E. 2011. Medindo a diversidade biológica. Editora UFPR, Curitiba, Brazil.

Marques, J. G. W. 2002. O olhar (des)multiplicado. O papel do interdisciplinar e do qualitativo na pesquisa etnobiológica e etnoecológica. Pages 31-46 in M. C. M. Amorozo, L. C. Mingg, and S. M. P. Silva, editors. Métodos de coleta e análise de dados em etnobiologia, etnoecologia e disciplinas correlatas. UNESP/CNPq, Rio Claro, Brasil.

Mbete, R. A., H. Banga-Mboko, P. Racey, A. Mfoukou-Ntsakala, I. Nganga, C. Vermeulen, J. L. Doucet, J. L. Hornick and P. Leroy. 2011. Household bushmeat consumption in Brazzaville, the Republic of the Congo. Tropical Conservation Science 4(2):187-202.

Medici, E. P., K. Flesher, B. M. Beisiegel, A. Keuroghlian, A. L. J. Desbiez, A. Gatti, A. R. M. Pontes, C. B. Campos, C. F. Tófoli, E. A. Moraes Júnior, F. C. Azevedo, G. M. Pinho, J. L. P. Cordeiro, T. S. Santos Júnior, A. A. Morais, P. R. Mangini, L. F. Rodrigues, and L. B. Almeida. 2012. Avaliação do risco de extinção da anta brasileira Tapirus terrestris Linnaeus, 1758, no Brasil. Biodiversidade Brasileira 1:103-116.

Medri, Í. M., G. M. Mourão, and F. H. G. Rodrigues. 2011. Ordem Cingulata. Pages 75-84 in N. R. Reis, A. L. Peracchi, W. A. Pedro, and I. P. Lima, editors. Mamíferos do Brasil. Universidade Estadual de Londrina, Londrina, Paraná, Brasil.

Melo, R. S., O. C. Silva, A. Souto, R. R. N. Alves, and N. Schiel. 2014. The role of mammals in local communities living in conservation areas in the Northeast of Brazil: an ethnozoological approach. Tropical Conservation Science 7(3):423-439.

Meserve, P. 2007. Zoogeography of South America. Pages 112–132 in A. Orme, editor. Physical geography of South America. Oxford University Press, Oxford, UK.

Mesquita, G. P., and G. P. Barreto. 2015. Evaluation of mammals hunting in indigenous and rural localities in Eastern Brazilian Amazon. Ethnobiology and Conservation 4:1-14. http://dx.doi.org/10.15451/ec2015-1-4.2-1-14

Milner-Gulland, E. J., and E. L. Bennett. 2003. Wild meat: the bigger picture. Trends in Ecology & Evolution 18(7):351-357. http://dx.doi.org/10.1016/S0169-5347(03)00123-X

Ministério do Meio Ambiente (MMA). 2014. Espécies ameaçadas - lista 2014. MMA, Brasilia, Brazil. [online] URL: http://www.icmbio.gov.br/portal/biodiversidade/fauna-brasileira/lista-de-especies.html

Miranda, C. L., and G. D. S. Alencar. 2007. Aspectos da atividade de caça no Parque Nacional Serra da Capivara, estado do Piauí, Brasil. Natureza & Conservação 5(1):27-34.

Miranda, F., N. Moraes-Barros, M. Superina, and A. M. Abba. 2014. Tolypeutes tricinctus. IUCN Red List of Threatened Species, Cambridge, UK. [online] URL: http://www.iucnredlist.org/details/21975/0

Mockrin, M. H., R. F. Rockwell, K. H. Redford and N. S. Keuler. 2011. Effects of landscape features on the distribution and sustainability of ungulate hunting in northern Congo. Conservation Biology 25(3):514-525. http://dx.doi.org/10.1111/j.1523-1739.2011.01660.x

Myers, N., R. A. Mittermeier, C. G. Mittermeier, G. A. B. da Fonseca, and J. Kent. 2000. Biodiversity hotspots for conservation priorities. Nature 403:853-858. http://dx.doi.org/10.1038/35002501

Oliveira, J. A., P. R. Gonçalves, and C. R. Bonvicino. 2003. Mamíferos da Caatinga. Pages 275-302 in I. R. Leal, M. Tabarelli, and J. M. C. Silva, editors. Ecologia e Conservação da Caatinga. Universitária da UFPE, Recife, Brasil.

Parliamentary Office of Science and Technology. 2005. The bushmeat trade. POSTnote 236:1-4

Pereira, J. P. R., and A. Schiavetti. 2010. Conhecimentos e usos da fauna cinegética pelos caçadores indígenas “Tupinambá de Olivença” (Bahia). Biota Neotropica 10(1):175-183. http://dx.doi.org/10.1590/s1676-06032010000100018

Pezzuti, J., and R. P. Chaves. 2009. Etnografia e manejo de recursos naturais pelos índios Deni, Amazonas, Brasil. Acta Amazonica 39(1):121-138. http://dx.doi.org/10.1590/s0044-59672009000100013

Phillips, O., and A. H. Gentry. 1993. The useful plants of Tambopata, Peru: I. Statistical hypotheses tests with a new quantitative technique. Economic Botany 47(1):15-32. http://dx.doi.org/10.1007/BF02862203

Posey, D. A. 1986. Introdução a Etnobiologia: teoria e prática. Suma Etnológica Brasileira 1:15-25.

Prance, G. T. 1987. Vegetation. Pages 28-44 in T. C. Whitmore and G. T. Prance, editors. Biogeography and quaternary history in tropical America. Oxford Science Publications, Oxford, UK.

Read, J. M., J. M. V. Fragoso, K. M. Silvius, J. Luzar, H. Overman, A. Cummings, S. T. Giery, and L. F. Oliveira. 2010. Space, place, and hunting patterns among indigenous peoples of the Guyanese Rupununi region. Journal of Latin American Geography 9(3):213-243. http://dx.doi.org/10.1353/lag.2010.0030

Robinson, J. G., and E. L. Bennett. 2004. Having your wildlife and eating it too: an analysis of hunting sustainability across tropical ecosystems. Animal Conservation 7(4):397-408. http://dx.doi.org/10.1017/s1367943004001532

Rodrigues, L. A., C. Leuchtenberger and V. C. F. da Silva. 2013. Avaliação do risco de extinção da ariranha Pteronura brasiliensis (Zimmermann, 1780) no Brasil. Biodiversidade Brasileira 3(1):228-239.

Rodrigues, M. T. 1996. Lizards, snakes, and amphisbaenians from the quaternary sand dunes of the middle Rio São Francisco, Bahia, Brazil. Journal of Herpetology 30(4):513-523. http://dx.doi.org/10.2307/1565694

Rosas-Ribeiro, P. F., F. C. W. Rosas and J. Zuanon. 2012. Conflict between fishermen and giant otters Pteronura brasiliensis in Western Brazilian Amazon. Biotropica 44(3):437-444. http://dx.doi.org/10.1111/j.1744-7429.2011.00828.x

Sampaio, E. V. S. B. 1995. Overview of the Brazilian caatinga. Pages 35-63 in S. H. Bullock, H. A. Mooney, and E. Medina, editors. Seasonally dry tropical forests. Cambridge University Press, Cambridge, UK. http://dx.doi.org/10.1017/cbo9780511753398.003

Schipper, J., J. Chanson, F. Chiozza, N. A. Cox, M. Hoffmann, V. Katariya, J. Lamoreux, A. S. L. Rodrigues, S. N. Stuart, H. J. Temple, J. Baillie, L. Boitani, T. E. Lacher Jr, R. A. Mittermeier, A. T. Smith, D. Absolon, J. M. Aguiar, G. Amori, N. Bakkour, R. Baldi, R. J. Berridge, J. Bielby, P. A. Black, J. J. Blanc, T. M. Brooks, J. A. Burton, T. M. Butynski, G. Catullo, R. Chapman, Z. Cokeliss, B. Collen, J. Conroy, J. G. Cooke, G. A. B. Fonseca, A. E. Derocher, H. T. Dublin, J. W. Duckworth, L. Emmons, R. H. Emslie, M. Festa-Bianchet, M. Foster, S. Foster, D. L. Garshelis, C. Gates, M. Gimenez-Dixon, S. Gonzalez, J. F. Gonzalez-Maya, T. C. Good, G. Hammerson, P. S. Hammond, D. Happold, M. Happold, J. Hare, R. B. Harris, C. E. Hawkins, M. Haywood, L. R. Heaney, S. Hedges, K. M. Helgen, C. Hilton-Taylor, S. A. Hussain, N. Ishii, T. A. Jefferson, R. K. B. Jenkins, C. H. Johnston, M. Keith, J. Kingdon, D. H. Knox, K. M. Kovacs, P. Langhammer, K. Leus, R. Lewison, G. Lichtenstein, L. F. Lowry, Z. Macavoy, G. M. Mace, D. P. Mallon, M. Masi, M. W. McKnight, R. A. Medellín, P. Medici, G. Mills, P. D. Moehlman, S. Molur, A. Mora, K. Nowell, J. F. Oates, W. Olech, W. R. L. Oliver, M. Oprea, B. D. Patterson, W. F. Perrin, B. A. Polidoro, C. Pollock, A. Powel, Y. Protas, P. Racey, J. Ragle, P. Ramani, G. Rathbun, R. R. Reeves, S. B. Reilly, J. E. Reynolds II, C. Rondinini, R. G. Rosell-Ambal, M. Rulli, A. B. Rylands, S. Savini, C. J. Schank, W. Sechrest, C. Self-Sullivan, A. Shoemaker, C. Sillero-Zubiri, N. De Silva, D. E. Smith, C. Srinivasulu, P. J. Stephenson, N. van Strien, B. K. Talukdar, B. L. Taylor, R. Timmins, D. G. Tirira, M. F. Tognelli, K. Tsytsulina, L. M. Veiga, J.-C. Vié, E. A. Williamson, S. A. Wyatt, Y. Xie, and B. E. Young. 2008. The status of the world’s land and marine mammals: diversity, threat, and knowledge. Science 322(5899):225-230. http://dx.doi.org/10.1126/science.1165115

Silvius, K. M., R. E. Bodmer, and J. M. V. Fragoso. 2004. People in nature: wildlife conservation in South and Central America. Columbia University Press, New York, New York, USA.

Smith, P. 2007. Southern Tamandua: Tamandua tetradactyla (Linnaeus, 1758). FAUNA Paraguay Handbook of the Mammals of Paraguay 3:1-15.

Souto, W. M. S., J. S. Mourão, R. R. D. Barboza, and R. R. N. Alves. 2011. Parallels between zootherapeutic practices in ethnoveterinary and human complementary medicine in northeastern Brazil. Journal of Ethnopharmacology 134:753-767. http://dx.doi.org/10.1016/j.jep.2011.01.041

Souza, J. B., and R. R. N. Alves. 2014. Hunting and wildlife use in an Atlantic forest remnant of northeastern Brazil. Tropical Conservation Science 7(1):145-160.

Statsoft. 2001. STATISTICA v6. User Manual/Tutorial. Statsoft, Tulsa, Oklahoma, USA

Trinca, C. T., and S. F. Ferrari. 2006. Caça em assentamento rural na Amazônia matogrossense. Pages 155-167 in P. Jacobi, and L. C. Ferreira, editors. Diálogos emambiente e sociedade no Brasil. Annablume, São Paulo, Brasil.

van Vliet, N., M. P. Q. Mesa, D. Cruz-Antia, L. J. N. Aquino, J. Moreno, and R. Nasi. 2014. The uncovered volumes of bushmeat commercialized in the Amazonian trifrontier between Colombia, Peru & Brazil. Ethnobiology and Conservation 3(7):1-11. http://dx.doi.org/10.15451/ec2014-11-3.7-1-11

van Vliet, N., and R. Nasi. 2008. Hunting for livelihood in northeast Gabon: patterns, evolution, and sustainability. Ecology and Society 13(2):33. [online] URL: http://www.ecologyandsociety.org/vol13/iss2/art33/

van Vliet, N., M. P. Quiceno-Mesa, D. Cruz-Antia, L. Tellez, C. Martins, E. Haiden, M. R. Oliveira, C. Adams, C. Morsello, L. Valencia, T. Bonilla, B. Yagüe, and R. Nasi. 2015. From fish and bushmeat to chicken nuggets: the nutrition transition in a continuum from rural to urban settings in the tri frontier Amazon region. Ethnobiology and Conservation 4:1-12. http://dx.doi.org/10.15451/ec2015-7-4.6-1-12

Vanzolini, P. E. 1996. A contribuição zoológica dos primeiros naturalistas viajantes no Brasil. Revista USP 30:190-238. http://dx.doi.org/10.11606/issn.2316-9036.v0i30p190-238

Veloso, H. P., A. L. R. Rangel-Filho, and J. C. A. Lima. 1991. Classificação da vegetação brasileira, adaptada a um sistema universal. Ministério da Economia, Fazenda e Planejamento, Fundação Instituto Brasileiro de Geografia e Estatística, Rio de Janeiro, Brasil.

Vié, J.-C., C. Hilton-Taylor, and S. N. Stuart. 2009. Wildlife in a changing world - an analysis of the 2008 IUCN Red List of Threatened Species. International Union for Conservation of Nature, Gland, Switzerland.

Vieira, W. L. S., G. G. Santana, and C. Arzabe. 2009. Diversity of reproductive modes in anurans communities in the Caatinga (dryland) of northeastern Brazil. Biodiversity and Conservation 18(1):55-66. http://dx.doi.org/10.1007/s10531-008-9434-0

Walther, B. A., and J. L. Moore. 2005. The concepts of bias, precision and accuracy, and their use in testing the performance of species richness estimators, with a literature review of estimator performance. Ecography 28:815-829. http://dx.doi.org/10.1111/j.2005.0906-7590.04112.x

Wilkie, D. S., M. Starkey, K. Abernethy, E. N. Effa, P. Telfer, and R. Godoy. 2005. Role of prices and wealth in consumer demand for bushmeat in Gabon, Central Africa. Conservation Biology 19(1):268-274. http://dx.doi.org/10.1111/j.1523-1739.2005.00372.x

Wright, S. J., K. E. Stoner, N. Beckman, R. T. Corlett, R. Dirzo, H. C. Muller-Landau, G. Nuñez-Iturri, C. A. Peres, and B. C. Wang. 2007. The plight of large animals in tropical forests and the consequences for plant regeneration. Biotropica 39(3):289-291. http://dx.doi.org/10.1111/j.1744-7429.2007.00293.x

Address of Correspondent:
Raynner Rilke D. Barboza
Rua Geraldo Soares De Almeida
Bairro Catolé
Campina Grande, Paraíba
Brazil
58410-4
raynner@live.com
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