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Cotinga 30 Curiosity killed the : arbitrary hunting of Harpia harpyja on an agricultural frontier in southern Brazilian Amazonia Cristiano Trapé Trinca, Stephen F. Ferrari and Alexander C. Lees Received 11 December 2006; final revision accepted 4 October 2007 Cotinga 30 (2008): 12–15

Durante pesquisas ecológicas na fronteira agrícola do norte do Mato Grosso, foram registrados vários casos de abate de harpias Harpia harpyja por caçadores locais, motivados por simples curiosidade ou sua intolerância ao suposto perigo para suas criações domésticas. A caça arbitrária de harpias não parece ser muito freqüente, mas pode ter um impacto relativamente grande sobre as populações locais, considerando sua baixa densidade, e também para o ecossistema, por causa do papel ecológico da espécie, como um predador de topo. Entre as possíveis estratégias mitigadoras, sugere-se utilizar a harpia como espécie bandeira para o desenvolvimento de programas de conservação na região.

With adult female body weights of up to 10 kg, The study was conducted in the municipalities Harpy Eagles Harpia harpyja (Fig. 1) are the New of Alta Floresta (09º53’S 56º28’W) and Nova World’s largest raptors, and occur in tropical forests Bandeirantes (09º11’S 61º57’W), in northern Mato from Middle America to northern Argentina4,14,17,22. Grosso, . Both are typical Amazonian They are relatively sensitive to anthropogenic frontier towns, characterised by immigration from disturbance and are among the first species to southern and eastern Brazil, and ongoing disappear from areas colonised by humans. fragmentation of the original forest cover. The Currently assigned to the IUCN category Near town of Alta Floresta was founded in 1976, since Threatened2, the species is now extinct in many when the environs have suffered high deforesta- parts of its original range, e.g. most of the Brazilian tion rates. By 2003, for example, only 37% of Atlantic Forest17, but is still widespread in original forest cover remained in the municipality Amazonia. south of the rio Teles Pires9. Nova Bandeirantes Despite their relatively large size, Harpy was initially colonised in 1981, but intensive Eagles are not typically hunted as game, although settlement commenced only in 1996. Despite the they are captured occasionally by indigenous loss of less than 15% of the municipality’s original hunters for ceremonial purposes3,17,18. However, forest by 2004, landowners have generally upheld during recent studies of hunting on a rural federal legislation, which limits deforestation to frontier7,20 in southern Brazilian Amazonia, several 50% of each property. interviewees reported Harpy kills, which are Hunting pressure in both municipalities is presented and discussed here. Whilst the extent of considerable, but most game species are still its effects on the local Harpy Eagle population is relatively abundant in Nova Bandeirantes20, unclear, such pressure undoubtedly constitutes an whereas some large-bodied species have been additional, possibly avoidable, impact on a extirpated near the town of Alta Floresta (F. relatively sensitive species. Michalski unpubl.). Despite large gamebirds such

Table 1. Records of Harpy Eagles Harpia harpyja shot by colonos in the municipalities of Alta Floresta, Juruena, Nova Bandeirantes and Nova Monte Verde, Mato Grosso, Brazil, gleaned from semi-structured interviews with local residents.

Municipality Evidence Motive Comments Alta Floresta Report Hunter unfamiliar with species Photograph Hunter unfamiliar with species Tarsus of livestock Photograph Predation of livestock Chickens Fig. 2 Perceived risk to livestock Report Perceived risk to livestock Skeleton Revenge against environmentally conscious landowner Juvenile shot at nest Juruena Fig. 3 Hunter unfamiliar with species Nova Bandeirantes Fig. 4 Hunter unfamiliar with species Hunter reprimanded by landowner Photograph Hunter unfamiliar with species Report Displaced nestling attacked agricultural worker Nova Monte Verde Report Perceived risk to pets and small children Eagle observed in the vicinity of house

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as being still abundant around Nova most livestock and virtually none to humans12. Bandeirantes19, the 14 hunters monitored trapped Some interviewees nevertheless reported raptors only , primarily ungulates, during the systematically decimating stocks6. seven-month study. Similarly, in Alta Floresta, On the other hand, Harpy Eagles play an gamebirds accounted for just 0.6% of responses in important role in the forest ecosystems they 149 interviews of rural households requested to inhabit, by regulating the populations of rank their five most important game species (F. mesopredators such as capuchins Cebus spp., which Michalski unpubl.). otherwise may contribute to cascade effects and Reports of hunted Harpy Eagles were obtained accelerate local extinctions of disturbance-sensitive ad. lib. from other informants during complemen- species11. Thus, removal of such arbitrary hunting tary research in the study area in 2000–07 (Table 1, pressure would undoubtedly contribute signifi- Figs. 2–4). In five cases (including a report from the cantly to long-term conservation. municipality of Juruena, contiguous with Nova If ignorance is the main enemy of the Harpy Bandeirantes), the eagle was killed simply to Eagle on the Amazonian frontier, education is satisfy curiosity. A possible contributory factor is surely its principal ally, and the same characteris- that most colonos are immigrants from rural south tics that attract the attention of the curious hunter, and east of Brazil, where Harpy Eagles are either i.e. its large size and prominent silhouette in the extremely rare extinct. In several instances, the forest canopy, can undoubtedly be part of a well- motive for killing the eagle was the perceived or planned education programme to not only satisfy actual risk to small livestock such as chickens. This the local population’s curiosity and eliminate was more apparent at Alta Floresta and may reflect misconceptions about the species, but to provide a depletion of the eagle’s natural prey due to habitat springboard for conservation initiatives in frontier fragmentation; Nova Bandeirantes still possesses municipalities. significant forest cover with natural Harpy prey The relative visibility of the Harpy Eagle, yet such as primates19 and Two-toed Choloepus mystique that surrounds it, support its potential didactylus21. For example, a pair of Harpy Eagles at adoption as a flagship for conservation programmes a nest within a degraded 230-ha suburban forest in the Amazon. In fact, its image is already fragment at Alta Floresta6 was suspected to be prominent in many societies: the Harpy Eagle is predating small-bodied livestock (B. Davis pers. the national bird of , where it features on comm.). However, a similar report is available from the country’s (Fig. 6), as it does on the municipality of Nova Monte Verde, east of Nova those of the Brazilian state of Paraná. The coat of Bandeirantes, which also has good forest cover. arms of Mato Grosso—in which Nova Bandeirantes As these reports were compiled informally, it is and Alta Floresta are situated—features a phoenix unclear how reliable a sample they represent of the (Fig. 6), which is remarkably similar to a Harpy frequency of such events in the region. Even if only Eagle, with its prominent of . Those of episodic, they could still impact negatively on the other major Amazonian states, such as Amazonas local Harpy Eagle population, given that a single and Pará, also depict eagles. In Brazil, state breeding pair may possess a home range of over 25 citizenship is valued almost as much as nationality, × 25 km1,12. However, most landowners were aware thus invoking partisan sentiments based on these of other instances of large forest eagles being shot symbols of statehood could offer a potential on neighbouring properties, and some may have strategy for disseminating interest and garnering declined to report their own actions given their support. illegality. Additionally, several other raptors, The involvement of local communities has including Crested Eagles Morphnus guianensis and proven successful in the conservation efforts for one Ornate Hawk-Eagles Spizaetus ornatus (Fig. 5) Brazilian bird species, Spix’s Cyanopsita were persecuted by smallholders in Alta Floresta spixii16, despite coming too late to save the species following the loss of livestock such as domestic from extinction in the wild, and lessons can be chickens. Ornate Hawk-Eagles are killed in Nova learned from projects of this type. Local ranchers Bandeirantes for the same reason (F. B. L. Palmeira may also be key conservation players on the pers. comm.). Amazonian frontier8, as well as elsewhere in South Unlike other apex predators such as America, where fiscal incentives may be one Panthera onca, Harpy Eagles are relatively easy potential strategy5,10. In the specific case of Nova targets for a hunter armed with a shotgun and Bandeirantes, the principal landowner (who motivated by fear or curiosity. are reprimanded a colono for shooting a Harpy) is naturally slow breeders—typically, one chick every highly respected by local residents because he has two years—compared to Jaguars, which breed supported colonisation programmes and donated annually and typically have multiple cubs. land. Persecution belies the fact that Harpies (again, As a flagship species, the Harpy Eagle would unlike Jaguars) constitute a negligible threat to obviously contribute to broader conservation

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Figure 2. Tarsus of adult Harpy Eagle Harpia harpyja shot in Alta Floresta, June 2005 (Alexander C. Lees)

Figure 1. Adult Harpy Eagle Harpia harpyja, Alta Floresta, July 2006 (Alexander C. Lees)

Figure 5. Mortally wounded adult male Ornate Hawk-Eagle Figure 3. Young Harpy Eagle Harpia harpyja shot in Juruena Spizatus ornatus and the chicken that cost it its life, Alta (Anon.) Floresta, July 2006 (Alexander C. Lees)

Figure 6. The coats of arms of Panama (left), and the Brazilian states of Paraná (middle) and Mato Grosso (right).

Figure 4. Adult female Harpy Eagle Harpia harpyja shot by a colono in Nova Bandeirantes (Leonar Dallagnol)

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objectives within the region. Whilst species such as 14. Rettig, N. L. (1978) Breeding behaviour of the H. harpyja are not yet officially endangered, there harpy eagle (Harpia harpyja). Auk 95: 629–643. can be no room for complacency. 15. Saab, R. (2006) Gavião real será integrado ao zoológico do Parque Chico Mendes. Acknowledgements www.riobranco.ac.gov.br/v3/index2.php?option We thank Leonar Dallagnol, Arley Brumati, Antônio =com_content&do_pdf=1&id=1550 (accessed Geraldo Conjiu, Francesca Belém Lopes Palmeira, October 2006). Carlos Peres, Vitória da Riva Carvalho and Geraldo 16. Schischakin, N. (1999) The Spix’s macaw conserva- Araújo. CTT is grateful to CAPES for a postgraduate tion program, a non-extinction story. Cyanopsitta stipend, SFF to CNPq for a research fellowship (no. 53: 12–15. 307506/2003–7) and ACL to the Natural Environment 17. Sick, H. (1997) Ornitologia brasileira. Rio de Research Council (UK) and Conservation Janeiro: Ed. Nova Fronteira. International (USA) for funding. 18. Socioambiental (2002) Parque Indígena do Xingu: homogeneidade e diversidade cultural. www.socioambiental.org/pib/epi/xingu/cultura. References html (accessed October 2006). 1. Alvarez-Cordero, E. (1996) Biology and conserva- 19. Trinca, C. T. (2004) Caça em assentamento rural no tion of the Harpy Eagle in Venezuela and sul do estado da Floresta Amazônica. M.Sc. Panama. PhD thesis. Gainesville: University of dissertation. Belém: Museu Paraense Emílio . Goeldi. 2. BirdLife International (2006) Harpia harpyja. 20. Trinca, C. T. & Ferrari, S. F. (2006) Caça em assen- 2006 IUCN Red List of threatened species. tamento rural na Amazônia matogrossense. In: www.iucnredlist.org (accessed October 2006). Jacobi, P. & Ferreira, L. C. (eds.) Diálogos em 3. Carvalho, J. C. M. (1949) Observações zoológicas no ambiente e sociedade no Brasil. São Paulo: Ed. rio das Mortes e no alto Xingu. Publ. Avulsos Annablume. Mus. Nac., 5: 7–19. 21. Trinca, C. T., Palmeira, F. B. L. & Souza Júnior, J. 4. Fowler, J. M. & Cope, J. B. (1964) Notes on the S. (2006) A southern extension of geographic harpy eagle in British Guiana. Auk 81: 257–273. distribution of the two-toed , Choloepus 5. Hoogesteijn, R. & Chapman, C. A. (1997) Large didactylus (Xenarthra, Megalonychidae). ranchers as conservation tools in the Venezuelan Edentata 7: 7–9. llanos. Oryx 31: 274–284. 22. Touchton, J. M., Hsu, Y. & Palleroni, A. (2002) 6. Lees, A. C. (2006) Gavião real: of eagles and men. Foraging ecology of reintroduced captive-bred Alula 12: 68–71. subadult harpy eagles (Harpia harpyja) on Barro 7. Lees, A. C. & Peres, C. A. (2006) Rapid avifaunal Colorado Island, Panamá. Orn. Neotrop. 13: collapse along the Amazonian deforestation 365–379. frontier. Biol. Conserv. 133: 198–211. 8. Lopes, M. A. & Ferrari, S. F. (2000) Effects of human colonization on abundance and diversity Cristiano Trapé Trinca of mammals in eastern Brazilian Amazonia. Departamento de Pesquisa, Reserva Brasil, Av. Dr Conserv. Biol. 14: 1658–1665. Silva Melo 520, apto. 606, Jardim Taquaral, CEP 9. Michalski, F. & Peres, C. A. (2005) Anthropogenic 04675–010 São Paulo, Brazil; and Departamento de determinants of primate and carnivore local Zoologia, Museu Paraense Emílio Goeldi, Belém, Pará, extinctions in a fragmented forest landscape of Brazil. E-mail: [email protected]. southern Amazonia. Biol. Conserv. 124: 383–396. 10. Palmeira, F. B. L. (2004) Predação de bovinos por Stephen F. Ferrari onças no norte do estado de Goiás. M.Sc. disser- Departamento de Biologia, Universidade Federal de tation. Piracicaba: ESALQ/Universidade de São Sergipe, São Cristóvão, Sergipe, Brazil. Paulo. 11. Palomares, F., Gaona, F., Ferreras, P. & Delibes, M. Alexander C. Lees (1995) Positive effects on game species of top Centre for Ecology, Evolution and Conservation, School predators by controlling smaller predator of Environmental Sciences, University of East Anglia, populations: an example with lynx, mongooses and rabbits. Conserv. Biol. 9: 295–305. Norwich, NR4 7TJ, UK. E-mail: [email protected]. 12. Peregrine Fund (2006) Conservation projects: The Maya Project. www.peregrinefund.org/ maya_project (accessed October 2006). 13. Redford, K. H. (1992) The empty forest. Bioscience 42: 412–422.

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