- Open Access
Understanding the motivations for keeping wild birds in the semi-arid region of Brazil
Journal of Ethnobiology and Ethnomedicinevolume 14, Article number: 41 (2018)
Birds are kept as pets around the world, and bird-keeping is an ancient and widespread practice, constituting one of the main reasons for the decline of some species. In the semi-arid region of Brazil, this practice is very common and continues despite being designated as illegal in recent decades.
This study aimed to identify the species and families of songbirds used as pets in the semi-arid region of Brazil, characterize the maintenance of the exploited species in captivity, and evaluate the sociocultural context associated with this practice.
Data were collected from a total of 62 wild bird-keepers in the study area through interviews using semi-structured forms and informal conversations.
A total of 34 bird species are bred as pets in the study area. Thraupidae was the most represented family in this study followed by Icteridae, and together, these families accounted for 61.7% of the local specimens. As reported by the respondents, birds are acquired by capturing them in rural areas or through local and regional markets. The number of species identified by the respondents did not differ according to respondent income, educational level, or age (p > 0.05). Maintaining these birds in cages includes some care, such as providing feed, medicine, and in some cases, training to improve their song or to learn songs from other species. The species with the highest use values (UVs) were Sporophila albogularis (UV = 0.83), Paroaria dominicana (0.82), and Sporophila nigricollis (0.79), indicating their importance as wild animal pets.
The birds reported in this study have strong cultural importance and high economic value for the people involved in bird-keeping. In this sense, ethnoornithological studies are fundamentally important since they can provide basic information to inform plans and actions to promote the conservation and sustainable management of local avifauna, including the essential element of environmental education strategies.
Birds are kept as pets around the world [1,2,3,4,5], and bird-keeping is an ancient and widespread tradition. However, this practice is considered one of the main reasons for the population declines of many species [6,7,8,9,10]. In particular, species of the order Passeriformes are kept as pets in cages, which is motivated by their distinct characteristics compared to other groups, including beautiful plumage and/or melodious singing .
Due to its large size and impressive biodiversity, Brazil has one of the most diverse avifauna in the world , including 1840 known bird species . Considered the third largest biome in Brazil , the Caatinga encompasses most of the northeast region and houses, among other vertebrates, 591 birds’ species . In the northeast of the country, maintaining birds in captivity is a common practice driven by the accessibility to several species that are kept as pets, especially passerines [10, 16]. In the semi-arid region of northeastern Brazil, keeping wild animals in captivity is as old as human occupation, and most ethnozoological research shows that birds are the most exploited group in the region, which is a major threat to the populations of many local species [1, 10, 17,18,19]. In this region (the Caatinga biome), birds are used for different purposes and have major social, economic, and cultural importance . Several species of passerines and parrots are kept by local residents for pleasure, companionship, and ornamentation . Keeping songbirds in cages, in both rural communities and urban areas [10, 12, 20,21,22], and the associated illegal trade has been identified as a major cause of the reduced population sizes of various species in Brazil [10, 20, 22,23,24,25,26,27,28,29,30].
Most of the research on the keeping and trade of wild birds is generally concentrated on points of sale, especially free-trade fairs. These studies involve animal apprehension by supervisory agencies including a wide range of wild bird taxa, with little detailed information on the capture and captive management of Passeriformes. This order includes songbirds and deserves special attention since it is the most exploited by clandestine commerce [23, 30,31,32,33].
In the municipality in which the present study was developed, it is common for songbirds to be captured and sold as pets to residents of both rural and urban areas, and this is illustrative of the situation in other municipalities of the Brazilian semi-arid region. In this context, the objective of this study was to identify the species and families of songbirds targeted by merchants and bird-keepers and to characterize the captive maintenance of these exploited species to answer the following questions. Is the number of species used locally associated with the age, income, or level of education of the respondents? Which factors influence the captive breeding of songbirds’ species in the surveyed region? Do endemic species tend to be better known and more commonly used by the respondents? What is the conservation status of locally exploited species?
The study was conducted in the municipality of Lagoa Seca (07° 10′ 15″ S latitude; 35° 51′ 14″ W longitude) in the State of Paraíba, Brazil (Fig. 1). The municipality has an area of 107,589 km2 and a population of 25,900 inhabitants, of which 10,570 are urban and 15,330 are rural dwellers , and its human development index (HDI) is 0.627, according to the Human Development Atlas . Lagoa Seca is in the Agreste Paraibano Mesoregion and the Borborema Plateau geo-environmental unit, and it is 109.4 km from the state capital of João Pessoa, Paraíba, Brazil. The vegetation in this unit is composed of sub-deciduous and deciduous forests that are typical of wilderness areas . The climate is rainy tropical hot and humid, i.e., class A, AS’ (Köppen classification). The main economic activities in the municipality are trade and agriculture.
Information was obtained by bird-keepers and bird-sellers from urban and rural Lagoa Seca through opportunistic visits from October 2015 to March 2017. Initially, the goal was to build trust with the first respondents through informal conversations, in which the nature and objectives of the research were explained, and consent to record the information was requested. Second, data on bird use were collected through semi-structured interviews supplemented by free-form interviews and informal conversations [37, 38]. The forms used in the interviews were designed to collect information on socioeconomic aspects (income, education, profession, and housing), the frequency and motives for bird use, the abundance of species in the region (very low, low, medium, and high), and information on the commercial aspects of bird-keeping. The socioeconomic data (income, age, and level of education) of the respondents are summarized in Table 1.
The forms also included questions regarding the training and maintenance of captive birds (bird-keeping period, cost estimates, and animal singing characteristics) and the best capture period during the year. Based on the first interviews, further respondents were selected using the “snowball” technique , by which the initial respondent indicates other respondents for the researcher to reach.
Much information was gathered from direct observations of non-member participants  in the capture, maintenance, purchase, and sale of wild birds among respondents as well as visits to free-trade fairs where birds are sold.
The birds mentioned by the respondents were identified as follows: (1) direct observations in the houses of the respondents or commercial establishments; (2) photographic records during interviews; (3) the use of the checklist-interview technique , in which photographs of birds are shown to respondents; (4) orientation by taxonomists familiar with the local avifauna; and (5) from prior ethnoornithological research in the region [1, 18, 32, 42]. Following species identification, the scientific nomenclature followed the guidelines of the Brazilian Ornithological Records Committee . The Brazilian List of Species Threatened with Extinction  and the International Union for Conservation of Nature (IUCN) Red List  were used to determine the conservation status of each species.
The use value (UV) (adapted from Phillips et al.  by Rossato et al. ) was calculated to illustrate the relative importance of each species as a function of each of its uses and was calculated as UV = ΣU/n, where UV is the value of a species, U is the number of mentions per species, and n is the total number of respondents. The UV of each species is only based on the importance attributed by the respondents and does not depend on any valuation of the researcher [47, 48].
Analysis of wealth estimates
An incidence matrix of the type of interviewee (lines) by the type of species (columns) was created, assigning the value of 1 for each species mentioned by a respondent and 0 for unmentioned species. The accumulation curves, in which the X-axis corresponded to the number of individuals interviewed and the number of species used, were randomized 100 times, and the mean values were calculated using the program EstimateS (version 8.2) . The Chao 1 and Jackknife 1 estimators were used to estimate the total number of species in an area from the sampled data.
Statistical analyses were performed to determine the relationships between socioeconomic factors (age, income, and education) and the richness of the species used by the respondents. To determine the relationship between age and education and the number of species used, Spearman correlations were performed for non-parametric data, and a Kruskal-Wallis (H) test was used to determine if income influenced species richness, adopting a 5% level of probability (p < 0.05) [50, 51]. All tests were performed using the program Paleontological Statistics (PAST 2.17c) .
Results and discussion
Estimated richness of captive wild bird species
Respondents mentioned a total of 34 wild bird species from two orders and 11 families used as pets in the study region. These animals were acquired through illegal trade and/or captured by respondents themselves. Such practice was not surprising since these birds are chosen by bird-keepers for their diverse colours and songs, ease of maintenance, and in some cases, ability to imitate human speech . These factors have led to preferences among bird-keepers for wild birds, especially passerines [10, 54,55,56].
The species richness recorded in the interviews (34 species) approximates that projected by the Chao 1 (36 species, 94.4%) and Jackknife 1 (39 species, 87.2%) estimators, demonstrating sample adequacy in relation to the number of interviews (Fig. 2). Regarding socioeconomic factors, no significant correlations were found between species richness and the age or education level of the respondents (p = 0.868 and p = 0.45, respectively). The Kruskal-Wallis test showed that the number of species mentioned did not vary according to income (H = 7.38, p = 0.111).
Birds kept as pets
Because of the variety of species, their colourful plumage, small size, ease of maintenance in captivity, ease of transportation, and excellent singing capacity [10, 57, 58], Passeriformes are the most common birds in the world of illegal bird-keeping and trade, and these factors also govern the choice of bird species in the study area, located in the semi-arid region of Brazil, where bird-keeping is mainly associated with cultural issues, becoming a challenge from a sustainable and conservationist point of view [18, 59]. The necessity to consider the sociocultural context in conservation actions of wild birds on this region has been evidenced in recent ethnoornithological studies, which confirm the strong usage of birds for breeding and commercial purposes in several Brazilian semi-arid zones, although the legislation prohibits the use of wildlife in the country [17, 18, 23, 32, 33, 42, 60,61,62,63,64,65,66].
Of the 34 species mentioned by the respondents, Passeriformes was the order with the largest number of species (n = 32) followed by Psittaciformes, of which only two species were mentioned, the Turquoise-fronted Amazon Amazona aestiva and the Cactus Parakeet Eupsittula cactorum (Table 2). Of the mentioned species, 33 are native to Brazil, and six of those are endemic: the White-naped Jay Cyanocorax cyanopogon, the Campo Troupial Icterus jamacaii, Dubois’s Seedeater Sporophila ardesiaca, the White-throated Seedeater Sporophila albogularis, the Red-cowled Cardinal Paroaria dominicana, and the Cactus Parakeet E. cactorum (the last three are endemic to the Brazilian Caatinga). The species Spinus yarrellii (Yellow-faced Siskin) is listed on the Brazilian Ministry of the Environment (MMA) and the IUCN Red List as “Vulnerable” [44, 67] (Table 2). The only non-native bird, Estrilda astrild that is commonly known as the St. Helena Waxbill, is an introduced species, but because it was introduced to Brazil long ago and has adapted well, the Brazilian Institute of the Environment and Renewable Natural Resources (IBAMA) has chosen to treat it as a wild species, so its capture and trade is also prohibited . Although few respondents (n = 34) reported keeping parrots as pets, those that did claimed that the demand for E. cactorum is very high in the region and that they acquired this species by purchase, including for resale, or received it as a gift. The Psittacidae family (which includes parrots, parakeets, and macaws) is strongly affected by global trade [4, 68,69,70]; it is the second most traded bird family in the world .
In the study region, the use of wild birds as pets is directly associated with trade. Most of the respondents (n = 47) stated that in addition to keeping the mentioned species as pets, they directly participated in their purchase and sale. However, only a few respondents (n = 15) said that they only keep birds as pets and that their participation in trade is limited to purchase at fairs in the adjacent municipality of Campina Grande, Paraíba, Brazil, or from local merchants.
The most common families mentioned by the respondents were Thraupidae, which corresponded to 61.7% of the locally used specimens, followed by Icteridae (Fig. 3). The preference for keeping species of these families as pets is often observed in other areas of Brazil [1, 18, 23, 32, 60, 71,72,73] and is likely because this family includes beautiful Brazilian birds with large vocal repertoires [74, 75]. In a study conducted on the avifauna seized and voluntarily delivered to the IBAMA Wild Animal Triage Centre in the city of Juiz de Fora in Minas Gerais State, Brazil, Gogliath et al.  found many specimens from the families Thraupidae, Icteridae, and Psittacidae, of which seedeaters (Sporophila sp.), Saffron Finch (Sicalis flaveola), Green-winged Saltator (Saltator similis), Chopi Blackbird (Gnorimopsar chopi), and White-eyed Parakeet (Aratinga leucophthalma) were the most frequently possessed by bird-keepers and bird-sellers. In the surveyed area, birds such as Zonotrichia capensis (Passerelidae), Cyanoloxia brissonii (Cardinalidae), and Turdus sp. (Turdidae) are highly sought after for cage breeding, as they stand out due to their beauty and song, besides being easily kept in captivity.
When asked which birds are the most difficult to find in the local environment, among the most mentioned were S. yarrellii, Sporophila angolensis, and I. jamacaii, and some respondents even stated that they had not seen S. yarrellii in the wild for a long time and that the species is currently rare in captivity. According to the respondents, there are several reasons for the local disappearance of these species including the deforestation of rural areas for agricultural production, pesticide application on legume seeds (which kills granivorous birds), and exploitation pressure for bird-keeping and bird-selling. Additionally, some respondents described cases where small farmers mix poison with corn bran and spread it over their crops to prevent birds from feeding on planted seeds, thus killing birds that feed on the poisoned bran.
Main species and use value (UV)
The importance of each species reported in the present study for bird-keeping purposes is reflected in the respective UVs (Figs. 4 and 5), which varied between 0.01 and 0.83. The most important birds were S. albogularis, P. dominicana, Sporophila nigricollis, Z. capensis, C. brissonii, Tangara sayaca, Sporophila lineola, Turdus rufiventris, Turdus leucomelas, and S. flaveola.
Birds of the genus Sporophila are widely distributed throughout South America and are highly appreciated for their beautiful singing capacity [76, 77]. The prevalence of birds in this genus mentioned as being captured to be kept in cages (especially S. albogularis, a species endemic to the Caatinga with the highest UV in this study (UV = 0.83)) has also been highlighted in other studies of bird-keeping, selling, and seizure throughout Brazil [1, 10, 23, 33, 60, 61, 78,79,80,81].
Another species that stands out among the most mentioned birds in ethnoornithological studies in Northeast Brazil is P. dominicana, an endemic of the Caatinga biome  that is a favourite of bird-keepers and bird-sellers for various reasons, including easy capture [18, 19, 32, 59, 62, 63, 82]. It had the second highest UV in this study (UV = 0.82).
Species in the Thraupidae family were mentioned the most in the present study, as highlighted by their UVs. As already discussed, the preference for this family is because it includes beautiful Brazilian birds with beautiful singing capacity. In a study of wild bird seizures in the state of Amazonas over 20 years (1992–2011), Nascimento et al.  reported that the family Thraupidae accounted for the most species. Thus, Thraupidae species are commonly kept in various regions of Brazil [79, 81, 83].
Acquisition and maintenance in cages
Respondents stated that they acquired their birds directly from the wild (capture) as well as from illegal trade at fairs or among local bird-keepers (most common practice) as well as those from other localities. This finding indicates the existence of a commercial network involving the municipality of Lagoa Seca and other municipalities.
According to the interviewees’ testimonies, birds are captured directly from nature using four techniques: “assaprão,” “visgo,” “arapuca,” and “redinha or assaprão de rede”, which are toward to different bird species, taking into account the size of the animal, food habit, and locations and times of the year for capture. Of the techniques used, the ones with greater citations were the assaprão (n = 35) and the visgo (n = 15). Detailed descriptions of these techniques can be consulted in previous studies [42, 66, 84]. These bird-catching techniques are widely used among breeders from various Brazilian semi-arid sites [18, 23, 33, 62, 64, 71, 84], making it possible to capture a large number of species used as pets.
Rural respondents capture birds throughout the year but prefer the rainy season because it is the breeding period for most birds when there is abundant food for many species, especially the genus Sporophila, members of which have been reported as caged birds in several studies in Brazil [1, 18, 33, 54, 61, 64, 85]. Among the species captured or sold for bird-keeping, males are the most sought after because they have greater singing capacity and more beautiful plumage than females. According to Ribeiro and Silva , the preference for male individuals has had a very large negative impact on the populations of target species because approximately 90% of bird species breed monogamously.
In addition to free markets and fairs, the purchase of songbirds for captivity breeding through illegal trade is also evidenced by obtaining and selling these animals at strategic sites, such as meeting places and in households of breeders and traders, in order to avoid attention of supervisory bodies, establishing a decentralized clandestine marketing network.
Most bird-keepers use cages, but some respondents also mentioned using aviaries, which have more space but house multiple individuals of different species and sizes, which can cause stress and even result in fighting among birds. According to the respondents, larger birds are kept in larger cages. In the study area, it is very common to find cages hanging from the ceiling and in front of the homes of bird-keepers as well as in commercial establishments, and people walk the streets with cages in hand (Fig. 6).
Cages are primarily crafted from wood and wire and designed to hold only one individual, except for Saffron Finches S. flaveola, which are locally known as “canários-de-briga” and whose cages are larger to accommodate pairs of birds in multiple compartments for fights. Some respondents claimed to produce cages for their own use as well as sale to other bird-keepers (Fig. 7), thus earning extra income and saving money when purchasing birds. The respondents further indicated that the quality of a cage is directly associated with the quality of a bird, that is, birds with more beautiful plumage and greater capacity for singing are housed in more beautiful cages.
In general, after songbirds are removed from their natural environment, they require management to adapt to a life in captivity, which requires a certain period of time. According to the respondents, newly captured birds are known as “bicho brabo” (wild beasts) because they are unused to captivity, do not sing, and struggle intensely inside the cage, sometimes injuring themselves. “Pássaro em ordem” (bird in order) is the local term for a bird that has become adapted to captivity and moulted and that sings well and often.
The ability to mimic other songbirds or song melodies is common among some species that are captured and sold locally, and it may strongly influence the commercial value of these species. For example, S. albogularis mimics the song of C. brissonii, and I. jamacaii mimics other species and musical melodies. To develop the song of a young S. albogularis, its cage is kept near that of a strong-singing adult C. brissonii until it faithfully reproduces the C. brissonii song; this training requires an average of 4 to 6 months. To develop the capacity for sound imitation in I. jamacaii, individuals of this species are kept in a room and forced to listen to CDs playing the preferred bird song or other music for hours. Similar training was observed by Gama and Sassi  in a study of aspects of the illegal commercialization of wild birds in the city of João Pessoa, Paraíba, Brazil, where newly captured or sold birds are exposed to recorded birdsong and a conspecific or heterospecific “teacher” bird.
Feeding is a crucial factor in the well-being and development of bird song and determines the success of captive management . All respondents in the study area reported that both song and plumage quality are influenced by the diet of the bird, so the respondents offer a balanced diet based on fruit, feed, seed, millet, and birdseed that varies by species. In some cases, respondents reported giving vitamin compounds and calcium-based medicines to maintain the health, song, and plumage of the birds (Fig. 8).
Cage maintenance (sanitation and the provision of water and food) is normally performed once a day, but during the moulting season, when the bird undergoes a change in plumage, it does not sing for a long time and is vulnerable to disease, thus requiring extra care including limited exposure to wind and other birds. At this stage, medicines and vitamins are added to the diet whenever possible . When questioned about food expenditures, respondents stated that the monthly cost is low, averaging $5.00 to $7.00 US since a 500-g package of birdseed, millet, or feed costs $1.00 US on average, but according to the respondents, this amount increases some when it is necessary to buy medicines and vitamin compounds, which can be bought in local feed stores along with feed.
In addition to this basic diet, some respondents reported using mealworms, Tenebrio molitor Linnaeus, 1758, locally known as “tenébrio” (Fig. 9), that the respondents rear in their homes. The larvae are used as a nutrient-rich food supplement that benefits the health and song quality of birds such as S. albogularis, S. angolensis, Z. capensis, S. nigricollis, I. jamacaii, P. dominicana (Linnaeus, 1758), C. brissonii, and S. flaveola.
Bird fights: “rinhas”
In addition to trapping songbirds to keep them in cages as pets, certain species are commonly used in bird fights in the northeast and other parts of Brazil; this is an illegal practice known locally as “rinhas” [10, 18, 23, 87, 88]. The main species for this purpose is S. flaveola, but C. brissonii and P. dominicana are also used. In the present study, many respondents indicated knowledge of this practice in the region, but only four said they engaged in this activity with S. flaveola. Fighting occurs in the presence of bird owners and other people, who place bets on the bird they believe will win, and according to the respondents, bets range from $10.00 to $167.00 US. Fights occur inside cages that have several compartments (Fig. 10) including a “cumbuco,” which is a movable compartment coupled to the inside of a cage that can accommodate a pair of birds. According to the respondents, female birds are necessary to “rile up” the males for these fights. After pairing the cages, the movable compartments are opened, giving the males access to each other, and the females exit to another compartment but remain visible to their male partners. The fight only ends when one of the birds attempts to flee or is badly injured. The opponent is declared victorious, and the birds are separated by their owners.
Trends and future perspectives
Keeping wild birds is an antique practice in Brazil , recorded in the first historical documents during the colonial period. This cultural activity has been persistent over time despite the prohibitions of environmental agencies in the last century , a situation that led this practice to occur clandestinely in a widespread way, especially in some regions of Brazil, as in the semi-arid Northeast. Our results reinforce this situation, revealing that bird-keeping has attracted the interest of many people, driving an illicit trade in wild birds. The issue is intensified by the lack of or little supervision by environmental agencies, and when birds become part of the illegal trade in region, which interconnects various cities and intensifies wild species exploitation as pets in surveyed area. As a result of this persistent illegal trade, associated to others problems as a habitat loss, many songbird species has become rare or endangered due to over-exploitation.
The future scenarios point to the clandestine maintenance of this practice in surveyed area and all other Brazilian regions, especially taking to account a financial crisis context with low investment in patrolling and inspection process by the government, and also, the illegal trafficking income represents an alternative profit for some wild bird traders. In view of this perspective, it is recommended more population studies regarding the bird species explored, educational policies aiming to highlights the various negative implications of raising animals as pets, and greater strategies against illegal trade in the region. Environmental education programmes should be directed to individuals involved in the practice of raising and trading wild birds, but also to students in schools and to the general public, through press and broadcast media.
The rich diversity of songbird species that are marketed and kept as pets in the study region reflects the availability of and easy access to these animals as well as their economic and cultural importance. However, the number of species mentioned did not vary with the income, level of education, or age of the respondents. It has been shown that admiration and appreciation for singing are the main reasons for the local exploitation and trade of birds. Due to their small size, ease of maintenance, and high singing capacity, species of the family Thraupidae have the highest UVs, and species endemic to the Caatinga biome, such as S. albogularis and P. dominicana, suffer greater pressure from illegal trade and captive bird-keeping. This family had the highest UVs among the species reported in this study, indicating that the populations of each of these species are at risk due to removal from their natural environment.
Whether purchased or captured, respondents prefer male birds since they have the greatest capacity for singing, so male individuals suffer greater pressure from use. The results also indicate that males can be trained to improve the quality of their singing, consequently increasing their commercial value, but maintaining these birds in cages requires substantial care to maintain their health and song quality. Another important use is the exploitation of the Saffron Finch, S. flaveola, for fighting (known locally as “rinhas”), a clandestine activity that provides entertainment and potential financial returns for people who place bets on the fights.
Although considered illegal in Brazil, the keeping and sale of songbirds among people of different ages is common in the semi-arid region of the country. In this context, ethnoornithological studies are fundamentally important since they can provide basic information to inform plans and actions for conservation and sustainable management of the local avifauna, including environmental education strategies as an essential element.
Certificate of Presentation for Ethical Consideration
Brazilian Ornithological Records Committee
Wild Animal Triage Centre
Human development index
Hospital Universitário Lauro Wanderley
Brazilian Institute of the Environment and Renewable Natural Resources
International Union for Conservation of Nature
Ministry of the Environment
Alves RRN, Leite RC, Souto WMS, Bezerra DMM, Loures-Ribeiro A. Ethno-ornithology and conservation of wild birds in the semi-arid Caatinga of northeastern Brazil. J Ethnobiol Ethnomed. 2013;9:14.
Harris JBC, Tingley MW, Hua F, Yong DL, Adeney JM, Lee TM, Marthy W, Prawiradilaga DM, Sekercioglu CH, Winarni N. Measuring the impact of the pet trade on indonesian birds. Conserv Biol. 2017;31(2):394–05.
Jepson P, Ladle RJ. Governing bird-keeping in Java and Bali: evidence from a household survey. Oryx. 2009;43:364–74.
Roldán-Clarà B, Lopez-Medellín X, Espejel I, Arellano E. Literature review of the use of birds as pets in Latin-America, with a detailed perspective on Mexico. Ethnobiol Conserv. 2014;3:1–18.
Su S, Cassey P, Vall-Llosera M, Blackburn TM. Going cheap: determinants of bird price in the Taiwanese pet market. PLoS One. 2015;10:1–17.
Burivalova Z, Lee TM, Hua F, Lee JS, Prawiradilaga DM, Wilcove DS. Understanding consumer preferences and demography in order to reduce the domestic trade in wild-caught birds. Biol Conserv. 2017;209:423–31.
Drews C. Wild animals and other pets kept in Costa Rican households: incidence, species and numbers. Soc Anim. 2001;9:107–26.
Thomsen JB, Edwards SR, Mulliken TA. Perceptions, conservation, and management of wild birds in trade. TRAFFIC International, WWF and IUCN, Cambridge; 1992.
Tidemann S, Gosler A. Ethno-ornithology: birds, indigenous people, culture and society. London/Washington: Earthscan/James & James; 2010.
Alves RRN, Nogueira EE, Araujo HFP, Brooks SE. Bird-keeping in the Caatinga, NE Brazil. Hum Ecol. 2010;38:147–56.
Tully TN Jr. Chapter 10—birds. In: Manual of exotic pet practice. Saint Louis: W.B. Saunders; 2009. p. 250–98.
Marini MA, Garcia FI. Bird conservation in Brazil. Conserv Biol. 2005;19:665–71. 13
Avibase—the world bird database. Clements, version 2017. 2018. Retrieved from http://avibase.bsc-eoc.org/checklist.jsp?region=BR&list=clements. Accessed 8 July 2018.
Moura ACDA. Primate group size and abundance in the Caatinga dry forest, Northeastern Brazil. Int J Primatol. 2007;28:1279–97.
MMA Ministério do Meio Ambiente - Caatinga. 2017. Retrieved from http://www.mma.gov.br/biomas/caatinga. Accessed 15 Apr 2017.
Olmos F, Silva WAG, Albano CG. Aves em oito áreas de Caatinga no sul do Ceará e oeste de Pernambuco, Nordeste do Brasil: composição, riqueza e similaridade. Papéis Avulsos de Zoologia (São Paulo). 2005;45:179–99.
Alves MM, Lopes SF, Alves RRN. Wild vertebrates kept as pets in the semiarid region of Brazil. Trop Conserv Sci. 2016;9:354–68.
Fernandes-Ferreira H, Mendonça S, Albano C, Ferreira F, Alves RRN. Comércio e criação de aves silvestres (Psittaciformes, Piciformes e Passeriformes) no Estado do Ceará. A Etnozoologia no Brasil: Importância, Status atual e Perspectivas. 2010;4:379–402.
Paixão RMC, Silvestre LC, Pessoa TSA, Sousa AEBA. Entre saberes e observações: a manutenção em cativeiro de Passeriformes silvestres em uma comunidade da Zona da Mata Paraibana. Atualidades Ornitológicas On-line. 2013;174:54–9.
Alves RRN. Relationships between fauna and people and the role of ethnozoology in animal conservation. Ethnobiol Conserv. 2012;1:1–69.
Mallet-Rodrigues F, Parrini R, Pacheco JF. Birds of the Serra dos Órgãos, state of Rio de Janeiro, southeastern Brazil: a review. Revista Brasileira de Ornitologia. 2007;15:05–35.
Ribeiro LB, Silva MG. O comércio ilegal põe em risco a diversidade das aves no Brasil. Ciência e Cultura. 2007;59:4–5.
Gama TP, Sassi R. Aspectos do comércio ilegal de pássaros silvestres na cidade de João Pessoa, Paraíba, Brasil. Gaia Scientia. 2008;2.
IUCN: International Union for Conservation of Nature (IUCN). Red list of threatened species. Version 2016.3. 2016. Retrieved from http://www.iucnredlist.org/. Accessed 5 Jan 2017.
Pizo M. A conservação das aves frugívoras. Ornitologia e conservação: da ciência às estratégias. Tubarão: Ed Unisul; 2001. p. 49–59.
Robinson JG, Redford KH: Neotropical wildlife use and conservation. 1991.
Sick H. Birds in Brazil. Princeton: Princeton Univ. Press; 1993.
Sick H. Ornitologia Brasileira, edição revista e ampliada por José Fernando Pacheco. Rio de Janeiro: Nova Fronteira; 1997.
Sick H, Teixeira D. Notas sobre aves brasileiras raras ou ameaçadas de extinção. Publi Avuls Mus Nac. 1983;1079.
Silva EM, Oliveira ELR, Lima VFS, Borges JCG, Porto WJN. Aves silvestres comercializadas ilegalmente em feiras livres da cidade de Arapiraca, Alagoas. Enciclopédia Biosfera. 2015;11:2045.
Gogliath M, Bisaggio EL, Ribeiro LB, Resgalla AE, Borges RC. Avifauna apreendida e entregue voluntariamente ao Centro de Triagem de Animais Silvestres (CETAS) do IBAMA de Juiz de Fora, Minas Gerais. Leonardo. 2010;1:3.
Licariao MR, Bezerra DMM, Alves RRN. Wild birds as pets in Campina Grande, Paraíba State, Brazil: an ethnozoological approach. An Acad Bras Cienc. 2013;85:201–13.
Rocha MSP, Cavalcanti PCM, Sousa RL, Alves RRN. Aspectos da comercialização ilegal de aves nas feiras livres de Campina Grande, Paraíba, Brasil. Revista de Biologia e Ciências da Terra. 2006;6:204–21.
IBGE: Instituto Brasileiro de Geografia e Estatística. 2010. Retrieved from http://www.cidades.ibge.gov.br. Accessed 15 Feb 2016.
PNUD: Programa das Nações Unidas para o Desenvolvimento. 2010. Retrieved from http://www.atlasbrasil.org.br/2013. Accessed 15 de Feb 2016.
Brasil: CPRM - Serviço Geológico do Brasil. Projeto cadastro de fontes de abastecimento por água subterrânea. Diagnóstico do município de Lagoa Seca, estado da Paraíba. Organizado [por] João de Castro Mascarenhas, Breno Augusto Beltrão, Luiz Carlos de Souza Junior, Franklin de Morais, Vanildo Almeida Mendes, Jorge Luiz Fortunato de Miranda. Recife: CPRM/PRODEEM; 2005. p. 10.
Alburquerque UP, Lucena RP, Cunha LC. Métodos e técnicas na pesquisa etnobiológica y etnoecológica. Recife: Ed I NUPPEA; 2010. p. 39–64.
Huntington HP. Using traditional ecological knowledge in science: methods and applications. Ecol Appl. 2000;10:1270–4.
Bailey K. Methods of social reached. 2nd ed. New York: The Free Press; 1982. p. 553.
Stebbins RA. Fitting in: the researcher as learner and participant. Qual Quant. 1987;21:103–8.
Alexiades MN, Sheldon JW. Selected guidelines for ethnobotanical research: a field manual. New York: New York Botanical Garden; 1996.
Bezerra DMM, Araujo HFP, Alves RRN. Captura de aves silvestres no semiárido brasileiro: técnicas cinegéticas e implicações para conservação. Trop Conserv Sci. 2012;5:50–66.
Piacentini VQ, Aleixo A, Agne CE, Maurício GN, Pacheco JF, Bravo GA, Brito GR, Naka LN, Olmos F, Posso S. Annotated checklist of the birds of Brazil by the Brazilian Ornithological Records Committee/Lista comentada das aves do Brasil pelo Comitê Brasileiro de Registros Ornitológicos. Revista Brasileira de Ornitologia-Braz J Ornithol. 2015;23:90–298.
IUCN: International Union for Conservation of Nature (IUCN).The IUCN red list of threatened species. Version 2017-1. 2017. Retrieved from www.iucnredlist.org. Accessed 5 July 2017.
Phillips O, Gentry AH, Reynel C, Wilkin P, Galvez-Durand B. Quantitative ethnobotany and Amazonian conservation. Conserv Biol. 1994;8:225–48.
Rossato SC, De LeitãO-Filho HF, Begossi A. Ethnobotany of caiçaras of the Atlantic Forest coast (Brazil). Econ Bot. 1999;53:387–95.
Albuquerque UP, Andrade LHC, Silva ACO. Use of plant resources in a seasonal dry forest (Northeastern Brazil). Acta Bot Bras. 2005;19:27–38.
Alves RRN. Animal-based remedies as complementary medicine in Brazil. Forsch Komplementmed/Res Complement Med. 2008;15:226–7.
Colwell R. Statistical estimation of species richness and shared species from samples, version 8.2. 0. In: User’s guide and application Google Scholar; 2009.
Kruskal WH, Wallis WA. Use of ranks in one-criterion variance analysis. J Am Stat Assoc. 1952;47:583–621.
Kruskal WH, Wallis WA. Errata: use of ranks in one-criterion variance analysis. J Am Stat Assoc. 1953;48:907–11.
Hammer H, HARPER D, Ryan P. PAST: paleontological statistics software package for education and data analysis. Palaeontol Electron. 2001;4:9.
Thomsen J, Brautigam A. Sustainable use of neotropical parrots. In: Neotropical wildlife use and conservation; 1991. p. 359–79.
Ferreira FS, Albuquerque UP, Coutinho HDM, Almeida WO, Alves RRN. The trade in medicinal animals in northeastern Brazil. Evid Based Complement Alternat Med. 2012;2012.
Souto WMS, Torres MAR, Sousa BFCF, Lima KGGC, Vieira LTS, Pereira GA, Guzzi A, Silva MV, Pralon BGN. Singing for cages: the use and trade of Passeriformes as wild pets in an economic center of the Amazon—NE Brazil route. Trop Conserv Sci. 2017;10:1–19.
Zardo EL, Behr ER, Macedo A, Pereira LQ, Lovato M. Aves nativas e exóticas mantidas como animais de estimação em Santa Maria, RS, Brasil. Revista Acta Ambiental Catarinense. 2016;11:33–42.
Birkhead T, Van Balen S. Bird-keeping and the development of ornithological science. Arch Nat Hist. 2008;35:281–305.
Nash SV. Sold for a song: the trade in southeast Asian non-CITES birds. Cambridge: Traffic Southeast Asia; 1993.
Alves RRN, Mendonça LET, Confessor MVA, Vieira WLS, Vieira KS, Alves FN. Caça no semi-árido paraibano: uma abordagem etnozoológica. A Etnozoologia no Brasil: Importância, Status atual e Perspectivas Volume. 2010;4:347–77.
Bezerra DMM, Araujo HFP, Alves RRN. The use of wild birds by rural communities in the semi-arid region of Rio Grande do Norte State, Brazil. Biorem Biodiv Bioavail. 2011;5:117–20.
Barbosa EDO, Silva MGB, Medeiros RO, Chaves MF. Atividades cinegéticas direcionadas à avifauna em áreas rurais do Município de Jaçanã, Rio Grande do Norte, Brasil. Biotemas. 2014;27:175–90.
Barbosa JAA, Nobrega VA, Alves RRN. Aspectos da caça e comércio ilegal da avifauna silvestre por populações tradicionais do semi-árido paraibano. Revista de Biologia e Ciências da Terra. 2010;10:39–49.
Nobrega VA. Apectos do uso e comércio de aves silvestres por populações tradicionais do agreste paraíbano. In: Anais do IX Congresso de Ecologia do Brasil; 2009. p. 3.
Alves RRN, Nogueira EEG, Araujo HFP, Brooks SE. Bird-keeping in the Caatinga, NE Brazil. Hum Ecol. 2009;38:147–56.
Souza JB, Alves RRN. Hunting and wildlife use in an Atlantic Forest remnant of northeastern Brazil. Trop Conserv Sci. 2014;7(1):145–60.
Fernandes-Ferreira H, Mendonça SV, Albano C, Ferreira FS, Alves RRN. Hunting, use and conservation of birds in Northeast Brazil. Biodivers Conserv. 2011;21:221–44.
MMA. Ministério do Meio Ambiente. In: Portaria no 444 de 17 de dezembro de (2014) Fauna Ameaçada; 2014. Retrieved from http://www.icmbio.gov.br/portal/faunabrasileira/lista-de-especies. Accessed 5 Dec 2016.
Cantú-Guzmán JC, Sánchez-Saldaña M, Grosselet M, Silva-Gámez J. Tráfico ilegal de pericos en México: una evaluación detallada. Washington, DC: Defenders of Wildlife; 2007.
Wright TF, Toft CA, Enkerlin-Hoeflich E, Gonzalez-Elizondo J, Albornoz M, Rodríguez-Ferraro A, Rojas-Suárez F, Sanz V, Trujillo A, Beissinger SR. Nest poaching in Neotropical parrots. Conserv Biol. 2001;15:710–20.
Roldán-Clarà B, López-Medellín X, de la Barca NC, Leyva C, Espejel I. Mexican birds use according to environmental officers. Ethnobiol Conserv. 2017;6:1–18.
Santos I, Costa-Neto E. Estudo etnoornitológico em uma região do Semi-Árido do estado da Bahia, Brasil. Sitientibus Série Ciências Biológicas. 2007;7:273–88.
Souza GM, Soares Filho AO. Comércio ilegal de aves silvestres na região do Paraguaçu e sudoeste da Bahia. Enciclopédia Biosfera. 2005;1.
Teixeira PHR, do Nascimento Thel T, Ferreira JMR, de Azevedo SM, Junior WRT, Lyra-Neves RM. Local knowledge and exploitation of the avian fauna by a rural community in the semi-arid zone of northeastern Brazil. J Ethnobiol Ethnomed. 2014;10:81.
Sick H. Ornitologia Brasileira. 3rd ed. Rio de Janeiro: Nova Fronteira; 2001.
Sigrist T: Avifauna brasileira: guia de campo Avis Brasilis. 2013.
Filloy J, Bellocq MI. Spatial variations in the abundance of Sporophila seedeaters in the southern Neotropics: contrasting the effects of agricultural development and geographical position. Biodivers Conserv. 2006;15:3329–40.
Mason NA. Diversification rates and phenotypic evolution in the neotropical seed-eaters (genus Sporophila). In: Society FO, editor. 129th stated meeting of the American ornithologists’ union, Jacksonville, University of Florida. Florida: Florida Ornithological Society; 2011.
Assis IA, Lima DC: Uma introdução ao comércio ilegal de aves em Itapipoca, Ceará. 2007.
IBAMA: Ibama devolve à natureza 275 mil animais em 13 anos. 2016. Retrieved from http://www.ibama.gov.br/noticias/58-2016/134-ibama-devolve-a-natureza-275-mil-animais-em-13-anos. Accessed 4 June 2017.
Nascimento CAR, Czaban RE, Alves RRN. Trends in illegal trade of wild bird in Amazona State, Brazil. Trop Conserv Sci. 2015;8:1098–113.
Nunes PB, Barreto AS, Franco EZ. Subsídios à ação fiscalizatória no combate ao tráfico de aves silvestres e exóticas em Santa Catarina. Ornithologia. 2012;5:26–33.
Pereira GA, Brito MT. Diversidade de aves silvestres brasileiras comercializadas nas feiras livres da Região Metropolitana do Recife, Pernambuco. Atualidades Ornitológicas. 2005;126:14.
Alves RRN, Lima JRF, Araujo HFP. The live bird trade in Brazil and its conservation implications: an overview. Bird Conserv Int. 2013;23:53–65.
Alves RRN, Mendonça LE, Confessor MV, Vieira WL, Lopez LC. Hunting strategies used in the semi-arid region of northeastern Brazil. J Ethnobiol Ethnomed. 2009;5:12.
Matias CAR, Pereira IA, Reis EMF, Rodrigues DP, Siciliano S. Frequency of zoonotic bacteria among illegally traded wild birds in Rio de Janeiro. Braz J Microbiol. 2016;47:882–8.
Allgayer MC, Cziulik M. Reprodução de psitacídeos em cativeiro. Revista Brasileira de Reprodução Animal. 2007;31:344–50.
Ayres OM. Os animais dos Campos Gerais (PR): Impactos ambientais noticiados pela imprensa regional. In: Publicatio UEPG: Ciências Biológicas e da Saúde, vol. 12; 2006.
Firmino AMS, Seixas G. O tráfico de animais silvestres no pantanal de Mato Grosso do Sul: caracterização e recomendações. In: Resumo executivo do relatório final do Projeto de Implementação de Práticas de Gerenciamento Integrado de bacia Hidrográfica para o Pantanal e Bacia do Alto Paraguai Campo Grande, Instituto Pantanal; 2003. p. 51.
Fernandes-Ferreira H, Alves RRN. The researches on the hunting in Brazil: a brief overview. Ethnobiol Conserv. 2017;6:1–6.
The authors thank the Brazilian Coordination for the Improvement of Higher Education Personnel (CAPES) for the scholarship granted to the first author. They especially thank all the interviewees who shared their knowledge as well as the Federal University of Paraíba (UFPB) Pro-Rectory of Research (PROPESQ/UFPB) for supporting the translation of this manuscript through the PROPESQ/UFPB No. 03/2017 internal call. We also thank Dandara Monalisa Mariz da Silva Quirino Bezerra for his valuable contribution in the analysis of taxonomic aspects.
Availability of data and materials
All data generated or analysed during this research are included in this published article.
Ethics approval and consent to participate
The research was approved by the Research Ethics Committee of the Hospital Universitário Lauro Wanderley (HULW) under the Certificate of Presentation for Ethical Consideration (CAAE) No. 50219015.2.0000.5183. All interviewers consent to participate.
The authors declare that they have no competing interests.
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